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THESE DE DOCTORAT DE L’UNIVERSITE PIERRE ET MARIE CURIE Spécialité : Géophysique Appliquée Pour obtenir le grade de DOCTEUR de L’UNIVERSITE PIERRE ET MARIE CURIE (PARIS 6) Sujet de la thèse : Contribution au développement de la résistivité complexe et à ses applications en environnement Présentée par Ahmad GHORBANI Soutenue le 2 mars 2007 devant le jury composé de : M. C. Camerlynck Maître de Conférences, Paris 6 Invité M. Ph. Cosenza Maître de Conférences, Paris 6 Invité M. N. Florsch Professeur, Université Paris 6 Directeur de thèse M. A. Revil Chargé de recherche, CEREGE Examinateur M. A. Tabbagh Professeur, Université Paris 6 Examinateur M. K. Titov Professeur, Uni. St. Petersburg Rapporteur Mme M. Zamora Professeur, Université Paris 7 Rapporteur

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Page 1: Contribution au développement de la résistivité complexe et à ses ... · We used CR1Dmode code published by Ingeman-Nielsen and Baumgartner (2006) as forward modeling. The graphical

THESE DE DOCTORAT DE L’UNIVERSITE PIERRE ET MARIE CURIE

Spécialité :

Géophysique Appliquée

Pour obtenir le grade de

DOCTEUR de L’UNIVERSITE PIERRE ET MARIE CURIE (PARIS 6)

Sujet de la thèse :

Contribution au développement de la

résistivité complexe

et à ses applications en environnement

Présentée par

Ahmad GHORBANI

Soutenue le 2 mars 2007

devant le jury composé de :

M. C. Camerlynck Maître de Conférences, Paris 6 Invité

M. Ph. Cosenza Maître de Conférences, Paris 6 Invité

M. N. Florsch Professeur, Université Paris 6 Directeur de thèse

M. A. Revil Chargé de recherche, CEREGE Examinateur

M. A. Tabbagh Professeur, Université Paris 6 Examinateur

M. K. Titov Professeur, Uni. St. Petersburg Rapporteur

Mme M. Zamora Professeur, Université Paris 7 Rapporteur

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Résumé: Ce mémoire est divisé en deux chapitres. Le premier chapitre présente une synthèse bibliographique sur la méthode de Polarisation Provoquée (PP). Il passe en revue les derniers résultats théoriques et expérimentaux et insiste sur les applications environnementales de la méthode Polarisation Provoquée Spectrale (PPS ou Spectral Induced Polarization ou SIP en anglais), encore souvent appelée résistivité complexe.

Le deuxième chapitre comprend cinq sous-chapitres. Dans un premier sous-chapitre, l'approche bayésienne est développée pour inverser les paramètres du modèle de Cole-Cole dans les domaines temporel et fréquentiel. Nous avons évalué la pertinence et la robustesse de la méthode des moindres carrés pour l’inversion des données issues de la méthode PP. Les résultats montrent que l'approche classique dans le domaine temporel ne peut pas mener à une évaluation appropriée des paramètres Cole-Cole. L'emploi harmonique de signal carré injecté à fin d’obtenir un plus large spectre n’est pas non plus satisfaisant. À l'opposé, les paramètres Cole-Cole sont mieux inversés dans le domaine fréquentiel.

Dans un deuxième sous-chapitre, nous avons conçu un algorithme d'inversion 1D par homotopie pour récupérer les paramètres du modèle Cole-Cole à partir des données de PPS. Cet algorithme permet de découpler les effets associés à la seule PP de ceux issus de couplages électromagnétiques parasites se produisant dans une large bande de fréquences. Nous avons employé le code numérique, CR1Dmod, développé initialement par Ingeman-Nielsen et Baumgartner (2006), résout le problème direct. L’interface utilisateur graphique, que nous avons conçue, facilite les entrées des données et des paramètres du modèle a priori, ainsi que la définition de la configuration géométrique du dispositif (géométrie des câbles). Nous présentons deux exemples synthétiques pour illustrer la récupération des paramètres spectraux à partir de données de résistivités complexes.

Dans un troisième sous-chapitre, la PPS est appliquée pour le suivi de l'infiltration d'eau dans un sol limoneux-argileux. L’infiltration a été réalisée à partir d’une pluie artificielle (à débit de pluie quasi-constant) et au cours de deux expérimentations, l’une menée in situ et l’autre sur une colonne de sol. Les expériences ont été basées sur l'acquisition couplée de données de tensiomètres et de spectres de PPS durant l’infiltration. Cette approche a confirmé l'existence d'une baisse significative de la phase (ou de la conductivité imaginaire) dans la partie haute fréquence du spectre (typiquement, 1-12 kHz) qui a été corrélée avec le remplissage d’eau dans des pores de diamètres compris dans la gamme de [30-85] m. Ces baisses de phase sont interprétées comme un effet de type Maxwell-Wagner. Les résultats de cette étude suggèrent que la méthode PPS serait en mesure de fournir des informations sur le remplissage par l'eau des plus gros pores et ainsi d’estimer indirectement des propriétés structurales.

Dans un quatrième sous-chapitre, la mesure de la résistivité complexe est employée pour le suivi de la teneur en eau et des microfissures induites thermiquement sur des échantillons quasi-saturés d'argillite. Les mesures de PPS ont été enregistrées durant deux trajets consécutifs en dessiccation: (a) le premier trajet a consisté en une phase de désaturation à l'air ambiant et (b) durant le deuxième trajet, les échantillons ont été soumis à quatre paliers de chauffe (température égale à 70, 80, 90 et 105 °C). Durant la phase de désaturation, l'amplitude de la résistivité complexe a été extrêmement sensible au changement de teneur en eau (un facteur de 3 à 5). Pendant la phase de chauffage, la résistivité a augmenté de deux ordres de grandeur comparativement à l'état initial. Les modèles Cole-Cole et Cole-Cole Généralisé sont les meilleurs modèles pour inverser respectivement les données de PPS pour la phase de désaturation et la phase de chauffage. Cependant, les résultats prouvent que le développement de l'anisotropie et les changements par conséquent de texture peuvent induire différentes signatures spectrales et processus de polarisation.

Dans le dernier sous-chapitre, le modèle empirique de Cole-Cole qui est très largement utilisé dans les études PP est employé pour l'étude de la compaction par dissolution sous contrainte de formations sédimentaires. Notre contribution dans cette étude a consisté à écrire l'algorithme nécessaire à l’application du modèle de Cole-Cole dans le domaine temporel.

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Abstract: After a review on induced polarization method, this work is divided in five

parts. The parts one to four deal with theory, laboratory and field studies of environmental applications

of the spectral induced polarization (SIP) method. Last part is devoted to Cole-Cole model parameters

that are applied to the compaction of quartz sands by pressure solution.

In a first part, Bayesian approach is developed to invert of the Cole-Cole model parameters in

the time or in the frequency domain. We evaluate whether standard least square methods are capable

to invert the induced polarization data. The Bayesian procedure results show that the classical time

domain approach cannot lead to a proper estimate of the Cole-Cole parameters. Using the harmonics

of square current signals to reach a broader spectrum than the classical time domain single current

injection cannot lead to estimate the Cole-Cole parameters. At the opposite, the Cole-Cole parameters

can be more correctly inverted in the frequency domain.

In a second part, we developed a homotopy inversion algorithm for recover the parameters of

Cole-Cole model from spectral induced polarization (SIP) data in a 1D earth. Both induced

polarization and electromagnetic coupling effects occur simultaneously in a certain frequency

bandwidth. We used CR1Dmode code published by Ingeman-Nielsen and Baumgartner (2006) as

forward modeling. The graphical user interfaces allows easy entering the data and the a priori model

and also cable configuration. We present two synthetic examples to illustrate that the spectral

parameters can be recovered from multifrequency complex resistivity data.

In a third part, SIP is used for monitoring the water infiltration in a silty clay loamy soil in

both in situ and soil column experiments. These experiences were based on the coupled acquisition of

tensiometer data and SIP spectra during a water infiltration achieved by a artificial constant rainfall.

This approach confirmed the existence of a significant phase angle (or imaginary conductivity of SIP

data) drop in the high-frequency domain during an infiltration cycle that were correlated with the

water filling of pores in the [30-85] m diameter range. These phase drops are qualitatively interpreted

as a Maxwell-Wagner effect. The results of this study suggest that the SIP method would be able to

give valuable information about the water filling of bigger pores and to estimate indirectly soil

structural properties.

In a fourth part, SIP is used for monitoring the evolution of the water content and the thermally-

induced microcracks measured on four nearly water-saturated argillite samples. The SIP

measurements recorded during two consecutive desiccation paths: (a) the first path consisted in a

desaturation phase under ambient air and (b) during the second path; the samples were heated in a

temperature range of 70 to up 105 °C. The amplitude of the complex resistivity was extremely

sensitive to water content change (a factor of 3 to 5). During the heating phase, the resistivity

increased by more than two orders of magnitude compared to the initial state. Cole-Cole model and

the general Cole-Cole model are the best models to invert the SIP data for the desaturation phase and

the heating phase, respectively. However, the results show that the development of the anisotropy and

consequently textural changes can induce different spectral signatures and polarization processes.

In the last part, empirical Cole-Cole model that is largely used in induced polarization studies is

used to study of compaction of quartz sands by pressure solution. Our contribution in this study

involves the forward algorithm created in first part to solve Cole-Cole model in time domain.

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Table of contents

Preface.................................................................................................................................... 1

General introduction....................................................................................................... 3

Chapter 1: Spectral Induced Polarization: State of the art ......................... 7

1) Brief history of Spectral Induced Polarization....................................................... 9

2) Principles of Spectral Induced Polarization.......................................................... 12

3) Complex resistivity instrumentation....................................................................... 14

3-1) The SIP-FUCHS II laboratory and field equipment.............................................. 15

3-2) Sample holders and Electrodes ............................................................................... 16

4) Complex resistivity parameters ............................................................................... 21

5) Origins of Induced Polarization............................................................................... 22

5-1) Electrical double layer (EDL) ................................................................................. 22

5-2) Interfacial polarization (Maxwell-Wagner effects) ................................................ 24

6) IP models....................................................................................................................... 25

6-1) Empirical IP models ................................................................................................ 26

6-1-1) Cole-Cole model .................................................................................................. 26

6-1-2) Constant phase angle model (CPA or Drake model) ........................................... 29

6-1-3) Generalized Cole-Cole model (GCC) .................................................................. 30

6-2) Electrochemical (EDL)-based models .................................................................... 30

6-2-1) Electrode polarization in soils and rocks with mineral particles.......................... 31

6-2-2) Membrane polarization (Marshall and Madden, 1959) ....................................... 32

6-2-3) Vinegar and Waxman model (1984) .................................................................... 34

6-2-4)Granular models versus Capillary model (Titov et al., 2002) ............................... 35

7) Environmental IP applications ................................................................................ 38

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7-1) Permeability estimation ........................................................................................... 38

7-2) SIP measurement in vadose zone............................................................................ 43

7-3) Detection of contaminations in vadose zone and in ground water ........................ 44

7-3-1) Organic contamination of ground water ............................................................. 44

7-3-2) Contamination and SIP studies ........................................................................... 46

7-3-3) SIP studies of the effects of microbial processes .................................................. 49

7-3-3-1) Effects of Microbial Processes ........................................................................... 49

7-3-3-2) SIP laboratory studies of the effects of microbial processes ................................... 53

7-3-3-3) SIP field studies of the effects of microbial processes ............................................ 54

8) Conclusion .................................................................................................................... 56

9) References ..................................................................................................................... 58

Chapter 2: Papers........................................................................................................... 67

Paper1: Ghorbani, A., Camerlynck, C., Florsch, N., Cosenza, P. and Revil, A., Bayesian

inference of the Cole-Cole parameters from time and frequency domain

induced polarization, Geophysical Prospecting, in press 2007....................................... 69

Paper 2: Ghorbani, A., Camerlynck, C., Florsch, N., CR1Dinv: A Matlab program to

invert 1D Spectral Induced Polarization data for Cole-Cole model include

electromagnetic effects, Submitted for Computers and Geosciences, Feb. 2007. ....... 107

Paper3: Ghorbani, A., Cosenza, P., Ruy, S., Doussan, C. and Florsch, N., Noninvasive

monitoring of water infiltration in a silty clay loamy soil using Spectral Induced

Polarization, submitted.for Water Resources Research, April 2007 .............................. 129

Paper4: Cosenza, P., Ghorbani, A., Florsch, N. and Revil, A., Effects of drying on the

low-frequency electrical properties of Tournemire argillites, Pure and Applied

Geophysics, in press, 2007. ................................................................................................ 175

Paper5: Revil, A., Leroy, P., Ghorbani, A., Florsch, N. and Niemeijer, A. R., Compaction

of quartz sands by pressure solution using a Cole-Cole distribution of

relaxation times, Journal of Geophysical Research, vol. 111, B09205,

doi:10.1029/2005JB004151, 2006. 209

General conclusion and perspectives .................................................................. 221

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Preface

This work was supported by the INSU-ECCO program (Polaris II project, 2005-2007)

in France, a project in which I am participating. This project, which studies the application

and development of conventional induced polarization and spectral induced polarization, is a

collaboration between four laboratories: UMR Sisyphe (Department of Applied Geophysics at

University Pierre and Marie Curie), CEREGE (Department of Hydrogeophysics at the

University of Aix Marseille III), EGID (Department of Environment, Geo-engineering and

Development in the University of Bordeaux III) and EOST (University Louis Pasteur in

Strasbourg).

I would first like to express my gratitude to INSU (Institut National des Sciences de

l'Univers) for their continuing support in the Polaris II project. I would also like to thank the

Ministry of Science, Research and Technology in Iran and the SFERE (Société française

d'exportation des ressources éducatives) for granting me the PhD. scholarship that has made

my work possible.

I wish to acknowledge Professor Alain Tabbagh, Director of UMR Sisyphe, who has

created a scientific and friendly environment conducive for implementing research projects.

I thank my advisor Professor Nicolas Florsch for his continuous support in the Ph.D.

program. Nicolas was always there to listen and to give advice. He is responsible for

involving me in the Polaris-II project in the first place. He taught me how to formulate

questions and express my ideas. Nicolas taught me different ways of looking at inversion

problems.

I have greatly profited from the generous advice of Professor Albert Tarantola

regarding the inversion problem course and from his published works. My cordial thanks for

these and for the helpful discussions about inversion problems we had.

Special thanks go to assistant professor Philippe Cosenza who helped me to write this

dissertation as well as helping me with the challenging research that lies behind it. Philippe

has been a friend and mentor. He taught me how to write academic papers, made me a better

programmer, had confidence in me when I had doubts, and brought out the good ideas in me.

Without his encouragement and constant guidance, I could not have finished this dissertation.

He was always there to meet me and talk about ideas, to read proofs and mark up our papers,

and to ask me the right questions to steer me through my problems.

Thanks also to assistant professor Christian Camerlynk who guided my studies in

signal processing and inversion problems. He showed me different ways to approach a

research problem and the need to be persistent to accomplish any goal.

I would like to thank research director André Revil, coordinator of the Polaris-II

project, who helped me for scientific and linguistic editing of papers. I also extend my

gratitude to Claude Doussan and Stephane Ruy, researchers in INRA (Institut National de la

Recherche Agronomique) in Avignon.

I thank all my colleagues and friends in the UMR Sisyphe and Polaris-II project.

Finally, I sincerely thank my family, particular my wife Parisa, for her invaluable

support and patience throughout this project.

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General introduction

Induced polarization (IP) is an electrical geophysical method in which the electric field is

generated by feeding low-frequency current, generally 0.1 to 10 Hz, between a pair of

grounded electrodes and where the potential is then measured by another pair of grounded

electrodes. Mineral-electrolyte interfaces in the presence of an external electric field produce

electrode polarization of electrochemical origin. Non-mineralized soils and rocks also exhibit

a weaker background IP that is sometimes called membrane polarization.

The DC-electrical method is based on in-phase conductivity and is associated with the

conduction occurring in-phase with the reference electric current. However, the measured

electrical impedance is in general a complex quantity with both an in-phase and out-of-phase

or quadrature component (e.g., Keller and Frischknecht, 1982; Ward, 1990). In the frequency

domain, this out-of-phase conduction is related to a phase shift between the measured voltage

and the applied alternative current. Out-of-phase or quadrature conduction at low frequencies

(typically from 10 mHz to 10 kHz) is referred to in geophysics as complex resistivity. When

the spectra of these complex quantities are measured, the method is called Spectral Induced

Polarization (SIP). However, the amount of information obtained at each point in a SIP survey

(amplitude | | and phase shift ) compared to a DC-method (resistivity ) is very large.

Although data processing, data inversion and modeling of SIP data are difficult, SIP

measurement is very useful, for example, for discriminating the spatial variability of clay

from the spatial variability of salinity. Induced polarization phenomena increase with clay

content but decrease with salinity, whereas resistivity decreases with both clay content and

salinity (Slater and Sandberg, 2000).

IP was initially measured in the time domain (TD) – that is, the voltage decay after excitation

by a current pulse is measured. Recording spectra in the time domain is achieved by

measuring the voltage transient at a number of instants after the current pulse has been

switched off. This method was developed in the 1950s and has been extensively used in

mineral exploration. The frequency domain and time domain-induced polarization methods

are equivalent in a linear and causal system. Both of these methods are interrelated through

the Fourier transform (Tombs, 1981). Normally, in the conventional Time Domain IP method,

one hopes and expects to avoid the problem of EM coupling by using the “delay time”

(waiting for a suitable length of time, a few dozens of milliseconds) after the transmitter is

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switched off before starting to acquire useful data. During this delay it is expected that the EM

coupling will dissipate to negligible levels. However, IP measurements in the time domain do

not include wide-band spectral information. Duckworth and Calvert (1995) showed that time

domain integral chargeability that is obtained by integrating a voltage decay curve can be

misleading. Studies in mining geophysics surveying (e.g. Tombs, 1981) show that time

domain IP measurement is not capable of discriminating between graphite and sulfides or

between massive and disseminated sulfide deposits.

Moreover, electromagnetic (EM) coupling is a major impediment to the inversion of complex

resistivity and SIP data. EM coupling can be defined as the inductive and capacitive response

of the Earth, which manifests itself as a response over the IP signal. The effect is increased

when the survey is carried out over a conductive Earth or when the dipole length and dipole

spacings are large. However, EM coupling limits the SIP measurements in laboratory and/or

at least on small scales. EM coupling calculating corresponds to computing the mutual

impedance of the grounded transmitter and receiver circuits at the desired frequency in 1D,

2D or 3D. Usually, calculating mutual impedance is complicated and time-consuming.

More recently, IP and SIP have been applied in environmental problems, hydrogeophysics

(e.g., Kemna et al., 1999, Kemna et al., 2004). For example, in the case of water-saturated

sedimentary materials, SIP parameters are closely related to grain size distribution and to the

mean grain size of the medium (e.g., Chelidze et al., 1977; Chelidze and Guéguen, 1999;

Kemna, 2000). Moreover, the mean relaxation time of induced polarization is also known to

be closely related to the specific surface area of the porous medium (Binley et al., 2005).

When combined with the electrical formation factor, the mean relaxation time can be used to

determine the hydraulic conductivity of soils and rocks (Schön, 1996; Slater and Lesmes,

2002). In summary, although the SIP method has become increasingly popular in

environmental and groundwater investigations, its full potential has yet to be attained in

Environmental Geophysics.

The overall objective of this thesis is to develop the scientific basis for laboratory and field

measurements of IP effects. Three specific objectives have been defined:

1. To develop a specific inversion method in order to evaluate IP data acquisition

techniques in both the time and frequency domains.

2. To develop specific inversion algorithms that allow interpretation of field SIP data.

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3. To provide physical hypotheses for understanding the mechanisms of IP in soil and

clayey rocks.

To reach the first objective, we developed a Bayesian inversion approach. This method

provides solutions in the form of probability densities of the parameters obtained from an

induced polarization model (see paper 1). Regarding the second objective and as mentioned

above, EM coupling is a major impediment to the interpretation of complex resistivity and IP

data. Therefore, we will use the 1D forward modeling code written by Ingeman-Nielsen and

Baumgartner (2006b) in order to propose new inversion algorithms that take into account EM

coupling (see paper 2).

The third objective centers on two experimental studies performed with two different

materials: agricultural, silty, clayey, loamy soil and argillaceous rocks (argillites). First, an

experimental investigation was undertaken to study the ability of the SIP method for

monitoring water infiltration in a clayey loamy soil. It was based on the combined acquisition

of tensiometric and SIP data during water infiltration modeled by artificial constant rainfall

(see paper 3). Second, SIP measurements were performed on nearly water-saturated argillite

samples which were cored from an underground facility located at Tournemire (Aveyron,

France). These samples were subjected to desiccation phases to simulate the thermal loading

and hydric disturbance associated with deep nuclear waste storage (see paper 4).

The thesis is divided into two chapters. The first chapter contains a bibliographical review of

the SIP method. We present a brief history of the method and focus on environmental

applications such as indirect determination of in situ permeability and detection of

contaminants in aquifers and in the vadose zone. The second chapter contains five papers.

Paper 1 is a development of the Bayesian inversion for the time and frequency domains of

induced polarization. The second paper describes an inversion algorithm to invert SIP

parameters in the presence of EM coupling. The third and fourth papers present experimental

investigations performed in two geomaterials that are involved in environmental applications:

agricultural, silty, clayey, loamy soil and argillaceous rocks (argillites). The fifth paper uses

the time-domain Cole-Cole model to study the problem of compaction of quartz sands by

pressure. A forward modeling routine for the time-domain Cole-Cole model is used in the

inversion process.

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Chapter 1: Spectral induced polarization: State of the art

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1) Brief history of Spectral Induced Polarization

The Induced Polarization (IP) and Spectral Induced Polarization (SIP) developments before

1990 that are described in this section, are taken from Collett (1990). Electrical polarization

effects in soils and rocks were first recognized by Dr. Conrad Schlumberger in 1911 at Ecole

des Mines in Paris. Early in 1911, Schlumberger conducted a study of the electrical properties

of ore samples and rocks. Using alternating current in the audible frequency, he performed

experiments in watertight tanks holding water of various salinities. In 1912, he shifted from

the laboratory to actual field conditions at Val Richer, Normandy. In the laboratory the mutual

induction between the current and measuring circuits was negligible. However, in the field, he

found a strong interference between the lines. To overcome this problem he switched to direct

current and used a galvanometer as a potential measuring device. However, he experienced

another problem when using direct current – that is, the polarization effect occurring on the

copper potential electrodes. Since this imbalance made his measurements unreliable, he

designed and built a non-polarizing type of potential electrode, and the resistivity sounding

technique was born. In 1913, while prospecting for highly conductive metalliferous ore

bodies, Schlumberger noticed that after the current was switched off, small but measurable

potential differences continued for some time. It seemed to him that the ground was polarized

by the direct current and then discharged. He remembered that during his experimentation at

Val-Richer, while working above an iron water-supply pipe buried close to the surface, it had

affected his readings. From this observation, he reasoned that a metallic mass, or metal-like

conductive ore, could be distinguished from the surrounding rocks by this type of

polarization. By sending a direct current into the ground, interrupting the current and

measuring the polarization effect, he had developed a new prospection method for detecting

metallic conductors such as pyrite, pyrolusite and galena. In 1920 his first work describing the

electrical method of prospecting was published (Schlumberger, 1920). In this book, Chapter

VIII is entitled “Induced Polarization”.

Because of the measurement technology equipment available in those days, it was difficult to

measure IP signals accurately. During the 1930s and 1940s the IP method was tested widely

in oil exploration in USA and the former USSR. Time-domain IP studies continued in the

1940s in USA. In 1947 in Utah, scientists developed the long time-constant fluxmeter to filter

out the high frequency noise and allow visual observation of the integral of the decay. Low-

grade disseminated mineralization such as porphyry copper deposits were particularly

successful targets for IP surveys (Sumner, 1976). Seigel (1959) calculated a mathematical

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formula for overvoltage and normal IP response over layered media and over spheres for

several electrode arrays. The use of the term “chargeability”, referred to as “m”, could be

attributed to Seigel. Wait (1959) almost single-handedly laid the mathematical foundation for

the time and frequency domain for IP and electromagnetic (EM) prospecting.

Up to 1950, all IP measurements were in the time domain. In 1950, Seigel showed that the

apparent resistivity of a rock sample containing sulfides decreased markedly with increasing

frequency. The frequency domain technique was theoretically investigated by Wait but not

experimentally. because the power and sensitivity of the equipment available at that time were

inadequate. In 1956-1959, Madden and Marshall conducted a range of laboratory research and

basic theoretical studies of IP effects due to nonmetallic causes. They also defined the terms

“electrode polarization” and “membrane polarization”. Madden and Cantwell (1967) in the

equivalent circuit representation of the IP phenomenon used the Warburg impedance.

Vacquier et al., (1957) attempted to apply IP techniques to groundwater exploration. IP

effects were attributable to membrane polarization in “dirty” sands with a significant clay

content. Studies in the frequency domain began in 1951 in the former USSR. From 1963,

various prototype instruments and methods for making precision amplitude and phase

measurements of IP at very low frequencies were designed. After these research projects in

the 1950s, the IP method became widely established in the exploration for sulfide

mineralization.

In the 1960s, IP investigations began to look at complex resistivity (amplitude and phase)

measurements for discriminating between sulfides and other conductors such as graphite or

between economic sulfides and pyrite. Working on laboratory samples, Fraser et al. (1964)

measured different spectra for a discriminated texture such as a rich dissemination with ore

veins and shaly sandstone. Zonge and Wynn (1975) also observed a systematic change in the

shape of the Cole-Cole plot with the alteration and degree of mineralization of a rock. Van

Voorhis et al. (1973) measured in-situ phase spectra of porphyry copper mineralization, but

concluded that the spectra were similar and that the broad-band response could be exploited

by recognizing and eliminating the effect of inductive coupling. Pelton et al. (1978) followed

up on these investigations. They found that two spectral parameters, chargeability and the

time constant, showed a wide variation between types of mineralization in an applied Cole-

Cole impedance model. They made small-scale in-situ measurements in ore outcrops in order

to discriminate sulfide ore from graphite and porphyry copper mineralization by its ore-

mineral grade and texture. This model has been extensively used in the field and has proved

reliable.

10

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During the 1980s, SIP was increasingly used for (a) petroleum industry and (b)

environmental applications. Concerning the petroleum industry, the IP technique has been

used to detect geochemical anomalies created by the presence of hydrocarbons at depth. The

hypothesis is that the IP anomalies measured above oil reservoirs are related to fine-grained

pyrite disseminations originating from hydrocarbons that have seeped from the reservoir.

Shaly reservoirs have been studied and specific models have been developed (Bussian; 1983;

Vinegar and Waxman, 1984; de Lima and Sharma, 1992).

Concerning environmental applications, Klein and Sill (1982) studied the effect of grain size,

electrolyte conductivity and clay content on the resistivity spectrum of artificial samples

composed of clay, glass beads and water. They found that the time constants approximately

follow the grain size of the glass beads.

During the 1990s, new laboratory SIP instruments capable of measuring phase spectra became

available and wide-band frequency devices were constructed for environmental applications.

Olhoeft (1984, 1985) obtained different kinds of phase spectra for clean and organically

contaminated clay samples, while Vanhala et al. (1992) and Vanhala (1997b) measured

complex resistivity in an attempt to map oil contamination in glacial till with a very low clay

mineral content. That team also observed a time dependence of the signals in polluted

samples, whereas measurements in uncontaminated samples were stable (Vanhala, 1997b).

Indeed, these measurements showed that the SIP method is sensitive to changes in grain

surface properties corresponding to organic contaminants.

Studies from long ago (e.g., Madden and Marshall, 1959; Klein and Sill, 1982) had already

shown that SIP data depend on pore-space geometry or grain size and on the microstructure of

the internal rock boundary layer. For this reason, they contain information about rock

permeability and fluid properties in the pore space. In recent years, SIP measurement was

used to determine hydraulic conductivity in the laboratory (Börner and Schön, 1991) and in

the field (Börner et al., 1996).

In the last decade, certain authors have traced a link between SIP and the mechanical

properties of soils and rocks (e.g., Lockner and Byerlee, 1985, Glover et al., 1997, and 2000).

Glover and colleagues showed the frequency dependency of the electrical properties of water-

saturated sandstones during triaxial deformation.

Much knowledge has been acquired since then on IP phenomena in hydrogeologic

investigations. Ulrich and Slater (2004) measured the complex conductivity responses of

unconsolidated sediments as a function of water/air saturation. Titov (2004) presented results

of laboratory time domain measurements conducted on sieved sands with different degrees of

11

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saturation and proposed a conceptual model to explain the experimental data. Binley et al.

(2005) showed the possible link between SIP and hydraulic properties in saturated and

unsaturated laboratory samples of sandstone. They also showed that the Cole-Cole model

gives a better data fit than the constant phase angle model used by Vinegar and Waxman

(1984) and Börner et al. (1996).

Understanding of the organic contamination of aquifers has accelerated recently by the use of

SIP measurements in the laboratory. For example, it is known that an increase in the

biological activities of microbes corresponds with higher levels of organic materials in

aquifers (Balkwill and Boon, 1997). Recent studies have shown that SIP measurements are

capable of assessing microbial activities so the method can be used to detect organic

contamination (e.g., Ntarlagiannis et al., 2005b; Abdel Aal et al., 2006).

However, other studies have shown that wider ranges of frequencies are necessary in order to

develop efficient model descriptions. One of the factors contributing to the underutilization of

IP methods is the need for careful wiring in order to prevent unwanted electromagnetic

coupling effects. Recent developments of remove or calculation of EM coupling response are

published by Routh and Oldenburg (2001) or Ingeman-Nielsen and Baumgartner (2006a and

2006b).

2) Principles of spectral-induced polarization

Electrical resistivity is measured by imposing an electric current I and measuring the resulting

electric potential or voltage V. The electric field is generated between a pair of grounded

electrodes, and the potential is measured by another pair of grounded electrodes, similar to the

DC resistivity method. The excitation signal can be constant in time (known as direct current

or DC) or alternating in time (known as alternating current or AC). During a DC

measurement, the resistance R is defined by Ohm’s law as the ratio of the voltage to the

current, i.e. V/IR . The resistivity parameter is derived from the measured resistance by

applying a sample geometric correction. For an AC measurement, the capacitance properties

of the medium must be taken into account in addition to the resistance per se. In this case,

Ohm’s law has been generalized to allow for the resulting frequency-dependent effects, and

the ratio of the voltage to the current, V/IZ , is known as the impedance rather than the

resistance. However, resistivity is often used for both DC and AC measurements.

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During an AC electrical resistivity measurement of soil or rock, the voltage measured at any

given frequency of excitation induces a phase lag in time relative to the excitation current

(Figure 1). To describe this effect, the output voltage can be expressed as the vector sum of

both in-phase (real) and out-of-phase (quadrature or imaginary) components. Therefore, the

electrical impedance Z of the medium can be expressed as a complex number where both the

magnitude and phase lag of the voltage relative to the input current depend on the specific

electrical properties of the sample. This is the origin of the term “complex resistivity”.

The resistivity and the amount of phase lag in the measured voltage signal is frequently a

function of the excitation frequency. In fact, in a first-order approach, the soil acts as a

capacitor in that it inhibits the passage of direct currents but passes alternating currents with

increased efficiency at higher frequencies.

Conventional induced polarization is an electrical geophysical method in which the electric

field is generated by feeding low-frequency current, generally 0.1-10 Hz. Induced polarization

can be measured in two ways. In the time-domain method (TD), the voltage decay after

excitation by a current pulse is measured (Figure 2), while in the frequency-domain method

(FD) it is the phase shift between injection current and voltage response that is measured. SIP

has been developed as an extension to conventional IP. In SIP the amplitude and phase

components of the earth’s resistivity are measured in a broad frequency range, typically 10-2

Hz to 104 Hz (Figure 1).

time

Am

pli

tud

e

Amplitude current I

measured voltage V

I

V0

log(freq.)

Am

pli

tud

e

Amplitude |

phase

-Ph

as

e

| =k*V/I

0

(a) (b)

Figure 1: Data acquisition in spectral-induced polarization. (a) A sinusoidal electric current I

of period T in a single frequency is imposed on a medium and the resulting voltage V is

measured. The measured voltage is characterized by a phase lag in time relative to the

excitation current. (b) Resistivity and phase spectrum. The ratio of voltage |V| to current |I|

multiplied by the geometric factor, K, expresses the magnitude (amplitude) of the complex

resistivity of the medium, where both its magnitude and the phase depend on the specific

electrical properties of the sample.

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time

IVoltage signal (V)

Current signal (I)

V

Vp

V

V0

V0

Vp

Vp

t1t2

Figure 2: Data acquisition in the time-domain-induced polarization method (TD). The voltage

decay after excitation by a current pulse is measured. By definition, the ratio of voltage

immediately after the current is shut off (Vp) divided by the maximum potential difference

measured during current transmission (V0) is known as chargeability M. Integral

chargeability, Ma, is the area under the decay curve between t1 and t2 times that is normalized

by the maximum potential difference measured during current transmission and (t2 - t1).

3) Complex resistivity instrumentation

In the laboratory, three different measurement systems are needed to measure the broadband

electrical impedance response from 10-3

Hz to 109 Hz:

(a) Four electrode systems are used to measure the impedance response from 10-3

Hz to104 Hz

because of electrode polarization in low frequency;

(b) Two-electrode systems are used to measure the impedance response from 102 Hz to10

7

Hz;

(c) Transmission line systems (e.g. TDR) are used to measure the impedance response from

106 Hz to10

10 Hz.

The effective frequency range of each of these measurement systems is limited by systematic

errors intrinsic to the measurement configuration. For each measurement system, it is possible

to have large systematic errors that are stable and repeatable but give erroneous results. It is

important, therefore, to test and calibrate these systems with known standards (e.g. standard

resistors and brines) to determine the overall accuracy of the measurements. It is not possible

to measure the complete broadband impedance response in the field with currently available

instrumentation (Lesmes and Friedman, 2005).

%orV

Vm

V

VM

0

p

120

t

t

p

attV

dttV

M

2

1

14

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3-1) The SIP-FUCHS II laboratory and field equipment

The SIP-FUCHS II instrument (Radic Research) operates in a frequency range from 1.4 mHz

to 12 kHz over 7 decades of frequency. To measure the whole spectrum, the SIP FUCHS-II

apparatus starts with the highest frequency, 12 kHz, and the N other decreasing frequencies

are obtained by the following division: 12 kHz/2N. It consists in two remote units that record

the current and voltage signal. The measured data are transferred to the base unit, where the

apparent resistivity and the phase shift are determined. The SIP-FUCHS-II is connected to a

computer, which enables real-time visualization of the results. The SIP-FUCHS-II can be also

used in the laboratory. For deep investigation, an external 600 W transmitter is preferred in

order to improve the signal-to-noise ratio (Figure 3). Optical fibers are used for data

transmission and system synchronization. This eliminates uncontrolled cross-coupling

between transmitter and receivers and increases the measuring accuracy because potential

cables can be shortened to the distance between the electrodes (Radic Research).

In laboratory experiments, we also used a complex resistivity system (1253 Gain-Phase

analyzer Solartron Schlumberger) to measure the frequency range from 1 mHz up to 20 kHz.

An example of SIP data acquisition is given in paper 3.

1 1

Figure 3: SIP-FUCHS-II: Laboratory and field equipment. 1) Base unit and PC for real-time

visualization of results. Built-in base unit 50 W transmitter, signal generation, data

management and synchronism. 2) Remote units for parallel current and voltage recording. 3)

External 600 W transmitter. 4) Generator.

4

1

3

2

15

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3-2) Sample holders and Electrodes

The main difficulty in measuring complex resistivity is to avoid electrode effects. Electrode

effects are as follows:

(a) Electrode polarization: this effect appears when the frequency responses of the

electrode (typically lower than 100 Hz) and the geomaterial are superposed. Electrode

polarizations may occur at the boundary between the sample and the measuring

electrodes (e.g., Vinegar and Waxman, 1984, Garrouch and Sharma, 1994; Levitskaya

and Stenberg, 1996; Carrier and Soga, 1999; Chelidze et al., 1999, Vanhala and

Soininen, 1995).

(b) Electrode-sample contact: when the electrode impedance is a dominant one, the

sample impedance is a small part of the total impedance and hence cannot be

measured with accuracy. This effect generally occurs in laboratory low frequency

measurements when dry and rigid samples are used.

There are methods to decrease the electrode effects for impedance measurements (Chelidze et

al., 1999). A maximal increase in the electrode-specific surface will significantly decrease

electrode impedance (e.g. Substitution technique where platinized electrodes are separated

from the sample by a contact electrolyte solution, Figures 4b and 4d).

1) Carrying out measurements at a minimal possible current intensity reduces

electrochemical reactions in the system.

2) Increasing the length of the sample to a maximum decreases distortions of the field in

the sample.

3) Cells with variable electrode spacing may be used (Figure 4a). As the electrode

impedance is the same for samples of different lengths, it can be excluded using the

subtraction of impedances, Z. The accuracy becomes low as impedance Z=0.

4) The four-electrode method may be used in which the measuring electrodes can be kept

away from the source electrodes. (Figures 4c and 4d).

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Direct Sample-electrode

contact

Substitution technique

Two-electrode

systems

(> 100 Hz)

(a) (b)

Four-electrode

systems

(c) (d)

Figure 4: simple schema of laboratory sample holders in complex resistivity measurement. (a)

Cell with varying sample length. 1-electrodes; 2-sample. (b) Substitution technique: 1-

platinized electrodes; 2-sample; 3-perforated diaphragm for holding sample; 4-contact

electrolyte solution. (c) Direct contact in four-electrode cell: 1- current electrodes; measuring

electrodes. (d) Four-electrode system with electrolytic cells preventing direct contact of

current electrodes with sample: 1-current electrodes; 2-measuring perforated electrodes; 3-

sample; 4-electrolytic compartments allowing convection of fluid; 5-sample holder (modified

from Chelidze et al., 1999).

Laboratory rock sample holders

The Binley et al. (2005) sample holder, which is a four-electrode system, consists in a 20-

mm diameter cylinder, copper disk current electrodes and Ag-AgCl non-polarizing electrodes

for potential measurements that are inserted into the holder arrangement. Binley et al. (2005)

filled the end cap reservoirs with the saturating fluid for water-saturated sandstone

measurements and filled it with a 4% agar-synthetic groundwater mix that prevented ingress

for unsaturated measurements (Figure 5).

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Figure 5: Sample holder arrangement for SIP measurements constructed by Binley et al.

(2005).

To minimize electrode effects simply, we used a four-electrode device that had low-cost

medical electrodes. The potential (or measuring) electrodes and the current (or source)

electrodes were electrocardiogram (ECG) Ag/AgCl electrodes (Asept Co.) and thin carbon

films (Valutrode® electrodes from Axelgaard Manufacturing Co.), respectively. Ag-AgCl

electrodes, which are known to be stable and almost non-polarizable in comparison with

metal electrodes, are widely used in laboratory SIP measurements (e.g. Vinegar and Waxman,

1984; Vanhala and Soininen, 1995). ECG Ag/AgCl electrodes consist of a small round metal

piece (10 mm diameter) galvanized by silver and covered with a soft sponge imbibed with

AgCl gel. The carbon films (50 mm diameter, 1 mm thick) that are used in electrotherapy are

circular and covered with a conductive adhesive gel to ensure a good electrical contact

between the electrodes and the rock sample (i.e. no air gaps in between). This four-electrode

device was validated by using porous and electrically inert samples (explained in paper 4)

(Figure 6).

20 mm

Rock

sample

60 mm

End chamber

(fluid or gel filled)

C+

P+

P-

C-

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Figure 6: Rock sample holder. 1) Potential electrodes: electrocardiogram (ECG) Ag-AgCl

electrodes. 2) Current electrodes: thin carbon films.

Laboratory soil sample holders

Olhoeft (1979a) used a four-electrode sample holder to measure the complex resistivity of soil

samples. The sample was divided into three parts each separated by through-going platinum

screen electrodes completely separating and covering the sample sections (Figure 7a).

Vanhala et al. (1992) used a four-electrode device where the sample was intact in a single

tube. The voltage electrodes were heavy-gage gold wires which penetrated only the outer skin

of the sample (Figure 7b).

Figure 7: Soil sample holders used by (a) Olhoeft (1979a) and (b) Vanhala et al. (1992)

(Figure taken from Brown et al., 2003).

1

2

19

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We designed and produced non-polarizing Cu/CuSO4 electrodes for use in SIP laboratory soil

electrodes in column infiltration monitoring (Figure 8). The porous ceramic has air pressure

entry value of 1.5 Bar. This electrode cannot be used in solutions with very low conductivity

(e.g. 200 S/cm).

Figure 8: Cu-CuSO4 non-polarizing electrodes used in experiment of infiltration on soil

column. The electrodes consist in: 1) porous ceramic; 2) flexible tube that is filled by

saturated CuSO4 solution; 3) copper wire; and 4) stopper.

Field electrodes

Metallic electrodes can be used as current-bearing electrodes for IP field deployment.

However, potential electrodes must be non-polarizing and their spectral response must not

overlap those of the signals to be measured. Usually, non-polarizing Cu/CuSO4 electrodes are

used in field IP as potential measuring electrodes. We used commercial ceramic porous

manufactured by Aquasolo that are used for watering (www.aquasolo.fr) and produced our

own non-polarizing Cu/CuSO4 electrodes for use in SIP field applications (Figure 9).

Figure 9: Potential electrodes for SIP field survey. These electrodes consist in a porous

ceramic (permeability: 7 cl/day) filled with Cu-CuSO4. We used commercial ceramic porous

devices made by Aquasolo that are used for watering (www.aquasolo.fr).

Porous ceramic

CuSO4 solution

Copper wire

stopper

1

2

4

3

20

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4) Complex resistivity parameters

The conductive and capacitive properties of a material can be represented by a complex

conductivity, , a complex resistivity, or a complex permittivity, , where

i1

(1)

and f2 is the angular frequency and 1i . Complex electrical parameters can be

expressed either in polar or rectangular form. For example, complex conductivity can be

expressed in terms of a magnitude, , and phase, , or real, and imaginary, ,

components:

iei

and (2)

1tan

The relationships between the real and imaginary components of complex resistivity and

conductivity are given by:

2

1 ,

and (3)

2

1

The other frequency domain-induced polarization parameters are percent frequency effect,

PFE and metal factor, MF defined by:

)(

)()(100

0

01PFE

and (4)

)()( 01aMF

and time-domain IP parameters are chargeability, M:

1

0

)(1

01max

t

t

dttVttV

M (5)

and normalized chargeability, MN (Lesmes and Frye, 2001):

MMN (6)

21

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where 0 a lower frequency and 1 a higher frequency; a a dimensionless constant; V(t) the

potential difference measured at a time t after the current is shut off, Vmax the maximum

potential difference measured during current transmission and t0 and t1 define the time

window over which the voltage decay curve is integrated.

The proportionality between the complex resistivity phase, , the percent frequency effect,

PFE, and chargeability, M, is both theoretically and experimentally well established (e.g.,

Marshall and Madden, 1959). These field IP parameters effectively measure the ratio of the

capacitive-to-conductive properties of the material at low frequencies. The low frequency

capacitive component, , is primarily controlled by electrochemical polarization

mechanisms, whereas the low frequency conductive component, is primarily controlled by

electrolytic conduction in the bulk pore solution. Therefore, field IP parameters are sensitive

to the ratio of surface conductivity to bulk conductivity effects. Metal factor and normalized

chargeability, MN are more directly related to the surface chemical properties of the material

and are therefore useful for characterizing lithological and geochemical variability (Lesmes

and Frye, 2001).

5) Origins of Induced Polarization

5-1) Electrical double layer (EDL)

When there is contact between solid and electrolyte media, the contact creates an ion

concentration gradient in the solution in the vicinity of the interface. Owing to the presence of

surface defects in their crystalline structure, the grains carry an excess often negative,

electrical charge compared to that inside the crystal. The interface thus attracts compensation

ions to restore electroneutrality. Under the effect of physical forces (Van der Waals) or

chemical (covalent) bonds, these compensation ions are adsorbed on the surface. The

effective charge of the ion atmosphere compensates the present surface charge and in

equilibrium between diffusive and electrostatic forces, the electrical double layer (EDL) is

formed at the interface between the solid and liquid phases (Figure 10) (Comparon, 2005).

Water and salt molecules bound to the rock surface constitute the Helmholtz or Stern layer,

which is sometimes divided into the inner Helmholtz plane (IHP) and the outer Helmholtz

plane (OHP) in order to include surface conductivity effects. In the IHP, salt and water

molecules are directly bound to the mineral structure. In the OHP, solvated salts are more

weakly bound to the mineral structure through higher-order interactions. In the OHP, it is

22

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assumed that ghee charges are free to migrate perpendicular to the particle surface and that

they may contribute to the DC conductivity of the mixture. However, it is impossible to

measure the amount of charge in the inner and outer layers (Ishido and Mizutani, 1981;

Lesmes and Morgan, 2001).

Ions in the electrolyte are affected by this electrical structure in a volume called the diffuse

layer, which by definition starts at a plane called the Stern plane. Far from the mineral

surface, the electrolyte can be considered to be unaffected and is therefore called the free

electrolyte. The charge densities in the diffuse layer are constrained by the surface charge

density in the Stern layer. The simplest theory of the EDL consists in neglecting the width of

the Stern layer and to model its charge density by a surface charge density concentrated on the

Stern plane.

Figure 10: Sketch of the structure of the electrical double layer in the three-layer model

(modified from Lorne et al., 1999; Chelidze and Gueguen, 1999). IHP, internal Helmholtz

plane; OHP, outer Helmholtz plane. The potential is defined as the electric potential at the

shear plane, located at a distance s from the Stern plane. Surface potential versus distance

from the solid surface x. 0 is the total potential drop between the surface of the solid and the

bulk of the electrolyte, s and are respectively potential drops in the Stern layer and in the

mobile part of the EDL and k-1

is the Debye screening length or thickness of the diffuse

double layer.

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The potential within the EDL is shown in figure 10, where the total potential drop 0

between the solid and the bulk of the electrolyte includes that in the diffuse, mobile part of the

EDL, which is usually called the potential and that in the dense, immobile part of the EDL,

which in turn includes the Stern potential s and the potential drop ( 0- s) due to chemically

bound non-solvated ions, which cannot be exchanged with the electrolyte. It is expected that

all ions that are at a potential field < s can be exchanged with the bulk of the electrolyte.

The Debye screening length or thickness of the diffuse double layer, k-1

, depends on various

parameters: electrolyte concentration, exchange cation valence, hydration ion size, solution

permittivity and pH. Increasing the electrolyte concentration and exchange cation valence

reduces the Debye length while increasing the hydration ion size, solution permittivity and pH

increases it.

5-2) Interfacial polarization (Maxwell-Wagner effects)

The second main origin of induced polarization in earth materials is geometrical and

interfacial. Spatial polarization results from differences in conductivity and polarizability

among components in a mixture, producing charge accumulation at the interface. The first

calculation concerning interfacial polarization was by Maxwell (1891) in his work on layered

materials. As Wagner (1924) solved the complex permittivity of a dilute suspension of

conductive spheres, interfacial polarization is also known as the Maxwell-Wagner effect. This

mechanism, which can be seen as a bulk effect, has a pure macroscopic definition and does

not require any comprehensive understanding of the physical process of charge accumulation

at the molecular level.

The best known formulation for modeling the Maxwell-Wagner effect is the Maxwell-

Wagner-Hanai-Bruggeman (MWHB) equation (e.g., Chelidze and Gueguen, 1999; Lesme and

Morgan, 2001), which corresponds to a Differential Effective Medium (DEM) theory (e.g.,

Cosenza et al., 2003). Consider a mixture of two components: spheroidal inclusions with an

effective complex permittivity i are embedded in a matrix characterized by an effective

complex permittivity m. The effective complex permittivity of the mixture mix is given by

the MWHB equation:

i

1/m

mix

m

mi

mixi d1 (7)

24

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where di is the volume fraction of spheroidal inclusions and m is a particle shape factor related

to the eccentricity of the spheroidal inclusions. It is also called the “cementation exponent”

(m=3 for spherical inclusions). Figure 11 shows an example of DEM theory for an initial

material with two phases. Moreover, it should be emphasized that the interfacial polarization

and the electrochemical models are not incompatible, since they operate at different scales.

For instance, Lesmes and Morgan (2001) proposed a granular model for the electrical

properties of saturated sedimentary rocks that combines both approaches. According to their

model, the MWHB equation was considered as a mixture formula in which the

electromagnetic properties of components, especially the clay fraction, are governed by

microscopic and physico-chemical laws.

Figure 11: An example of differential effective medium (DEM) theory. Homogenization

process in DEM theory: the initial material “m” corresponding to a relative permittivity km in

a volume V0. Phase “i” is embedded in phase “m” in such a way that the volume remains

fixed at V0. This is an iterative process that is continued until the volumetric fraction is

reached.

6) IP models

In this section, we review the empirical, theoretical and experimental models for complex

resistivity responses of rocks and soils and try to establish connections between the empirical

and theoretical parameters.

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6-1) Empirical IP models

6-1-1) Cole-Cole model

One of the most popular relaxation models is the Cole-Cole (C-C) model. It was first used in

geophysical prospecting by Pelton et al. (1978), but was originally developed by Cole and

Cole (1941) to describe complex permittivity behavior. In applied geophysics, Cole-Cole

resistivity dispersion is usually expressed in terms of complex resistivity (Pelton et al., 1978):

cim

)(1

111)( 0 (8)

Or as complex conductivity:

)1()(1

)(1)(* 0

mi

im

c

c

(9)

where 0 and 0 are respectively the resistivity and conductivity in the DC limit,

/1/ 000m is the chargeability, and are respectively the resistivity

and conductivity at high frequency, is the time constant, and c is the frequency dependence.

Pelton et al. (1978) showed that this model could be used to discriminate different types of

mineralization as well as the grain size of mineralized inclusions. The parameters 0, 0, m, c

and are obtained by fitting the model into the complex data. The parameter m describes the

magnitude of the polarization effect and is related to the relaxation time and indicates the

position (frequency) of the phase peak c

peak mf5.0

12/1 . The Cole-Cole phase spectrum

is symmetric and parameter c gives the slope of the phase spectrum in a double logarithmic

plot (Figure 12) (Major and Silic, 1981). The advantage in describing the dispersion of

resistivity in mineralized rocks lies in the similarity between the equivalent circuit (Figure 13)

exhibiting the impedance model and a model simulating the current paths in a mineralized

rock. In the equivalent circuit, resistance R0 corresponds to the resistance of the ohmic current

paths through the rock. The term c

Xi in series with resistance R1 describes the current

paths blocked by ore minerals. The term c

Xi is the complex impedance at the interface

between the ore minerals and the electrolyte, and resistance R1 is the resistance in the blocked

path.

In the Cole-Cole model for the equivalent circuit, parameters m and can be written (Pelton et

al., 1978) as 01 /1/1 RRm andc

RRX/1

10 . The characteristic frequency fpeak shifts

26

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towards higher frequencies when the value of m increases. Figure 14, that gives a plot of fpeak

versus c for different values of m, shows that if c is small and m large, the fundamental

relationship between the time constant and the phase maximum, e.g., peakf2/1 , disappears

totally (Vanhala, 1997a).

The Argand plot is a complex plane plot where the real and imaginary parts are usually

normalized by the real part of the measurement at the lowest frequency. Conventionally,

phases and imaginary parts are plotted with the sign reversed, yielding a positive phase peak.

The Argand diagram for C-C model is the arc of a circle (Figure 12c).

10-3

10-2

10-1

100

101

102

103

104

Frequency (Hz)

100

101

102

103

Am

plit

ud

e (

m)

0=1000 m

=0.05 sm=0.7c=0.7

100

101

102

103

-ph

ase

(m

rad

)

10-3

10-2

10-1

100

101

102

103

104

Frequency (Hz)

10-6

10-5

10-4

10-3

10-2

' (S

/m)

0=1000 m

=0.05 sm=0.7c=0.7

10-6

10-5

10-4

10-3

10-2

" (S

/m)

(a) (b)

10-3

2x10-3

2x10-3

3x10-3

3x10-3

4x10-3

' (S/m)

0x100

2x10-4

4x10-4

6x10-4

8x10-4

" (S

/m)

0=1000 m

=0.05 sm=0.7c=0.7

(c)

Figure 12: Different ways to display SIP results. (a) amplitude and phase shifts of spectra

when complex resistivity is used (C-C model), (b) real and imaginary conductivity of spectra

when complex conductivity is used (C-C model) and (c) Argand diagram of complex

conductivity.

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Figure 13: Mineralized rock and electrical equivalent circuit of Cole-Cole model connected.

R0 corresponds to the resistance of the ohmic current paths through the rock. Resistance R1 is

the resistance in the blocked path and cXi is the complex impedance at the interface

between the ore minerals and the electrolyte.

Figure 14: Dependence of the peak frequency fpeak, on c at different values of m in the Cole-

Cole model (Vanhala, 1997a).

The time domain analogue of the Cole-Cole equation (Pelton et al., 1978) describes the

transient IP characteristic during switching-off of the polarizing current at time:

0 )1(

)/()1()(

n

ncn

nc

tmtM (10)

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where 0/)()( VtVtM is time domain chargeability, V(t) and V0 are the potential value of the

decay curve at time t after shutting off the current and the potential just before shutting off the

current, respectively. (x) is the Gamma function. Parameters m, c and are C-C model

parameters.

However, in mineralized rocks, C-C parameters m and generally depend on the quantity of

polarizable elements and their size, respectively (Pelton et al., 1978; Luo and Zhang, 1998).

The exponent c depends on the size distribution of the polarizable elements (Vanhala, 1997;

Luo and Zhang, 1998). Binley et al. (2005) showed that there is a strong relationship between

C-C parameters determined in the frequency domain and the hydraulic conductivity of

saturated and unsaturated sandstone cores.

6-1-2) Constant phase angle model (CPA or Drake model)

Experimental investigations on rock samples have shown in several cases (porphyry copper

deposits, some sedimentary rocks) that complex resistivity data can appear as a straight line in

the Argand plot (Van Voohris et al., 1973; Vinegar and Waxman, 1984; Börner et al., 1993,

1996; Weller et al., 1996): the real and imaginary parts obey identical power laws of

frequency (Figure 15). Such data are represented in the so-called Drake model, also called the

Constant-Phase-Angle (CPA) model. This can be expressed by the equation (Pelton et al.,

1983):

ai )1(

1)(* 0 (11)

At high frequencies ( t >> 1), the amplitude is given by a)()(* 0 and the phase is

given by a2

.

Binley et al. (2005) examined the spectral IP response of samples taken from a UK sandstone

aquifer and compared the measured parameters with physical and hydraulic properties. They

showed that their SIP data were superposed with the C-C model.

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10-3

10-2

10-1

100

101

102

103

104

Frequency (Hz)

10-1

100

101

102

103

Am

plit

ude (

m)

0=1000 m

=5 sa=0.005

100

101

102

103

-phase (

mra

d)

920 940 960 980 1000

' ( m)

0

2

4

6

8

" (

m)

0=1000 m

=5 sa=0.005

(a) (b)

Figure 15: (a) An example of amplitude and phase shift spectra for the CPA model. (b) The

same example in an Argand diagram (CPA model).

6-1-3) Generalized Cole-Cole model (GCC)

To model an asymmetrical circular arc in the Cole-Cole representation, the Davidson-Cole

(D-C) model was proposed by Davidson and Cole (Davidson and Cole, 1950):

aim

)1(

111)(* 0 (12)

The C-C, CPA, and D-C models can also be generalized into a single formulation – that is, the

so-called generalized Cole-Cole model (GCC) (Pelton et al., 1983)

acim

))(1(

111)(* 0 (13)

When a=1 or c=1, one obtains the C-C model or the D-C model, respectively. When c=1 and

m=1, the CPA model is obtained. Klein and Sill (1982) showed that the GCC model is the

best model to fit the experimental data obtained from artificial clay-bearing sandstones.

6-2) Electrochemical (EDL)-based models

These type of models have been derived from a variety of diffusive polarization mechanisms

that can contribute to the complex conductivity response of water-bearing rocks and soils (e.g.

Marshall and Madden, 1959; Schwartz, 1962; Wong, 1979; Ward, 1990; de Lima and

Sharma, 1992) or of metal particle-electrolyte interface in rocks (Wong, 1979). In this

approach, the system consisting in an electrolyte-solid grain is characterized by a relaxation

time ( ) which is given by (e.g., Schwarz, 1962) =L2/2D , where D is the ion diffusion

coefficient and L is a characteristic length such as the mean grain size, pore size, the spacing

30

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between clay blockages of pore throats, or surface roughness (Lesmes and Friedman, 2005).

For earth materials, a relaxation time distribution must be taken into consideration.

6-2-1) Electrode polarization in soils and rocks with mineral particles

Wong (1979) attributes the polarization that occurs at a metal-electrolyte interface to two

mechanisms:

1) The polarization that results from the flow of inactive ions in the mobile part of the

EDL normal to the metal surface, resulting in the accumulation of inactive charge

excess or deficit near the metal surface.

2) The polarization that results from a minor concentration of redox-active ions in

solutions engaging in electrochemical reactions and allowing charge transfer across

the metal-electrolyte interface.

These mechanisms are illustrated in the conceptual model presented in Figure 16. In this

figure, the thickness of the EDL is grossly exaggerated for illustration; EDL electrochemical

theory assumes that the EDL thickness (1/ ) << grain radius r (Slater et al., 2005).

Figure 16: Conceptual model for possible polarization mechanisms in metal-particle-

containing soils such as sand-Fe0 mixtures. (a) No electric field; (b) application of electric

field. IP1 represents diffusion inactive ions normal to the metal surface; IP2 represents an

electrochemical reaction between metal (Mes) and metal ions in solution (Mex+

). Symbols are

r = metallic particle radius; 1/ = EDL thickness; )/1( kfrreff is the postulated

polarization sphere radius sensed with IP. EDL thickness is vastly exaggerated for the

purposes of illustration (EDL theory assumes 1/ <<r) (Slater et al., 2005).

31

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6-2-2) Membrane polarization (Marshall and Madden, 1959)

Membrane polarization is caused by the presence of clay particles (negative surface charge)

attracting positive cations from the pore water onto the negative surface, thereby forming

EDL. In the presence of pore constrictions, cationic clouds act as semi-permeable

electronegative membranes between adjacent sand grains. During application of an electric

current, these membranes locally enhance the transport of cations relative to anions, as shown

in Figure 17a. When the applied current is stopped, diffusion voltages that result from these

impressed concentration gradients decrease with time as the ions redistribute themselves to

position of equilibrium (Vinegar Waxman, 1984). In the membrane polarization model of

Marshall and Madden (1959), the sediment is described by two zones (selective and non-

selective) connected in series. The zones have different mobilities of cations and anions in the

electrolyte which, under applied external voltage, produce local charge accumulations and

charge density gradients causing the frequency dependence of the resistivity. In order for

polarization effects to occur, however, restrictive zones for anions are required (membrane

zones or selective zones), which are to be alternated with non-selective zones. A geological

analogy of this model is the shaly sand in which rock grains (quartz and other minerals) are

coated by a thin clay film; the water-filled interspaces form the non-selective zones while the

grain contacts are the selective zones.

Evidence now exists to show that membrane polarization affects are also significant and

measurable even in clay-free unconsolidated material when a low concentrated electrolyte is

used (Vanhala, 1997b, Titov, 2002).

This model predicts the following features:

The time constant increases as the length of the non-selective zone increases.

The model consequently predicts an increased time constant with increasing grain

size.

Membrane polarization decreases as pore-fluid salinity increases. This decrease can be

related to a decreasing thickness of the EDL with increasing fluid salinity.

Theoretically, this model provides the best understanding of IP phenomena in soils and rocks

but it has several parameters that limit its practical use. Klein and Sill (1982) showed that the

Davidson-Cole model fits with the Madden and Marshall model (Figure 18). Consequently,

better agreement is obtained when the empirical Davidson-Cole model is used.

Figure 17b shows an equivalent electric circuit for a membrane polarization model (Ward and

Fraser, 1967). The resistor Rw represents unblocked ionic sections of pore paths. The Warburg

impedance W represents the frequency-dependent diffusion impedance resulting from the

32

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membrane zones. Phenomenologically, the series resistance represents the electrolyte path in

series with the cationic clouds in Figure 17a and the bypass resistance represents leakage of

charge carriers around these zones.

(a)

(b)

Figure 17: (a) Schema of membrane polarization. (b) Equivalent circuit for membrane

polarization model. Rw is ionic solution resistance that represents unblocked ionic sections of

pore paths. W is Warburg impedance that represents the frequency-dependent diffusion

impedance resulting from the membrane zones (Slater and Sandberg, 2000).

10-3

10-2

10-1

100

101

102

103

1

2

3

0.9

0.8

0.7

0.6

0.5

Am

pli

tud

e (

m)

Madden-Marshall

Davidson-Cole

10-3

10-2

10-1

100

101

102

103

Frequency (Hz)

100

101

102

103

Ph

ase

(m

rad

)

Davidson-Cole parameters

=0.13 secm=0.24 a=0.5

R0=1 m

Amplitude

Figure 18: Comparison of Davidson-Cole model with the Madden and Marshall model where

L1=3.3*10-5

m, A=1, B=1, s1=1 and D1=2*10-9

m2/sec where L1 is length of non-selective

(clay free) zones, A is the ratio of zone lengths (length of non-selective zones divided by

length cation-selective zones), B=D1/D2 , D1 and D2 are diffusivity in non-selective and

selective (clay-bound) zones, respectively, and s1 are transference numbers in the selective

zones (modified from Klein and Sill, 1982).

Rw

Rw

W

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6-2-3) Vinegar and Waxman model (1984)

In DC resistivity studies, shaly sandstone samples show the significant surface conductivity

effects that result in a non-linear relationship between rock saturated conductivity and pore-

solution conductivity. Waxman and Smits (1968) modified Archie’s law to include a surface

conduction term in parallel with a bulk conduction term in saturation state:

surfaceweffF

1 (14)

where F is the electrical formation factor and w is the specific conductivity of the

equilibrating electrolyte solution (S/m). The formation factor can be estimated from the slope

of the linear portion of the eff versus w plot at high solution conductivity. Waxman and Smits

(1968) explained the effects of lithology and solution chemistry on the surface conductivity

term in the following model:

F

BQvsurface

and as: (15)

vweff BQF

1

where Qv is the cation exchange capacity of the rock divided by unit pore volume (meq.ml-1

)

and B is the equivalent ionic conductance of clay exchange cations as a function of w

(S.m2.meq

-1). Waxman and Smits (1968) empirically obtained the following formula for the

dependence of B on the solution conductivity:

wB exp1 (16)

where the fitting parameters , and depend upon the solution type.

Vinegar and Waxman (1984) measured the complex conductivity response of a suite of 21

shaly sandstone cores as a function of pore water conductivity. They used this data set to

develop the following complex form of the Waxman and Smits (1968) surface conductivity

model:

nF

QiBQ

Fi v

vweffeff.

1 (17)

where n is the fractional porosity. The parameter in Equation 17 represents an effective

quadrature conductance for these surface polarization mechanisms. Vinegar and Waxman

empirically determined to be slightly dependent on salinity. The polarization was assumed

to increase with decreasing porosity, as more pores become blocked.

34

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The real part of Equation 17 is the Waxman and Smits (1968) model, in which the bulk

and surface conduction terms are assumed to add up in parallel. The imaginary conductivity

results from displacement currents that are 90 degrees out-of-phase with the applied field

(Figure 19). Vinegar and Waxman assumed that the displacement currents were caused by the

following two polarization mechanisms:

1) The blockage of ions by clay minerals at pore throats (membrane polarization)

2) The accumulation of counter-ions migrating along the grain/pore surface.

Although these polarization mechanisms are intrinsically frequency-dependent, Vinegar and

Waxman showed that over the low frequency range of their measurements (3 Hz to 1 kHz),

the quadrature conductivity response was essentially independent of frequency. They assumed

that both of these polarization mechanisms were proportional to the effective clay content or

specific surface area, represented by the cation exchange capacity of the rock per unit pore

volume (Qv).

However, they also assumed that the phase angle is not dependent on using the frequency

range (CPA model) whereas consolidated rocks may display a distinct peak in the phase of the

conductivity spectra Cole-Cole model (Binley et al., 2005).

Figure 19: Complex conductance model for shaly sands in saturation state where F the

electrical formation factor, n the fractional porosity, w specific conductivity of the

equilibrating electrolyte solution (S/m), Qv cation exchange capacity of the rock divided by

unit pore volume (meq.ml-1

) and B equivalent ionic conductance of clay exchange cations

(modified from Vinegar and Waxman, 1984).

6-2-4) Granular models versus capillary model (Titov et al., 2002)

In induced polarization studies, the dominant relaxation time of the polarization has usually

been associated to grain size (namely Granular models) as shown in Figure 20a (e.g., Klein

and Sill, 1982; de Lima and Sharma, 1992; Chelidze and Guegen, 1999; Lesmes and Morgan,

2001). In the granular model (Figure 20a), a solid grain surrounded by its own ion atmosphere

35

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produces a local ion concentration gradient under the influence of electric current. The

concentration gradients give rise to ion flows, mostly represented by cations in the EDL. A

grain surrounded by its own ion atmosphere can be considered as the polarizing cell. The

relaxation time ( ) characterizing polarization of this cell is related to the ion diffusion

coefficient (D) and the grain radius (R), =R2/2D (Schwarz, 1962).

Titov et al. (2002) presented a theoretical relationship between ion-selective pore throats and

larger pores, again relating the IP mechanism to pore-throat size. They compared the behavior

of the model with experimental data obtained on natural sands (namely capillary models,

Figure 20b). Scott and Barker (2003) linked laboratory SIP measurements to pore-throat size

distributions obtained from mercury injection capillary pressure (MICP) tests on sandstone

samples. They suggested that the relaxation time is primarily associated with localized charge

blockage caused by constrictions in the fluid-filled pore space. Indeed, their experience

confirms the validity of the capillary model.

In the model by Titov et al. (2002) (Figure 20b), electric current produces local ion

concentration gradients in areas where the pore radii vary. The concentration gradients give

rise to ion flows, mostly represented by cations in throats, which produce a secondary out-of-

phase voltage. The sequence of large and narrow pores can be considered as the polarizing

cell. In this model, contacts of sand grains and inter-grain solution-filled space are considered

as electrical current passages of varying thickness, which differ in ion transport values. In the

model, sediments are likened to serial connection of active (ion-selective) and passive

(nonselective) zones. The model describes spectral IP characteristics for the medium where

the length of passive zones is much greater than that of active ones (Figure 21). The model is

called the short narrow pore (SNP) model. The authors used time-domain equations but

applied a Laplace-Carson transform and obtained the SNP model in the frequency domain as

follows (Figure 22):

5.0

5.0

0)(2

2exp111)(

i

im (18)

The SNP model predicts an increase in IP time constant as the length of ion-selective zone

increases. Its advantages are as follows. First the model has fewer parameters than the Cole-

Cole model, so the number of 2D and 3D SIP calculations that may be obtained is greater.

Second, the SNP model is a conceptual physical model whereas the Cole-Cole model is an

empirical model. However, the SNP model has to be validated for different type of soils and

rocks.

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Figure 20: schematic view of IP in ion-conductive rocks (modified from Titov, 2004). (a)

Scheme of electrical double layer at a negatively charged particle surface; (b) Schematic

distribution of cation and anion concentration outside the EDL; (c) Excess and deficiency in

ion concentration around a polarized changed spherical particle; (d) Excess and deficiency in

ion concentration along a polarized throat; diffusion flows and electric field same as in part

(c); (e) Schematic distribution of the ion concentration around a polarized spherical particle or

along a polarized pore throat; C* denotes the excess concentration produced by the polarizing

electric field.

Figure 21: Geometry of the electrical current pathway in sandy-clay sediments. 1l and 1l are

large-pore lengths and l2 is narrow- pore length (Titov et al., 2002).

37

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10-1

100

101

Frequency (Hz)

0

0.001

0.002

0.003

Ph

ase

(rad

)

SNP:=1 s, m=0.5%

Cole-Cole:=1 s, m=0.5%, c=0.62

SNP:=1 s, m=1%

Cole-Cole:=1 s, m=1%, c=0.62

Figure 22: Comparison between Cole-Cole and SNP models in frequency domain (modified

from Titov et al., 2002).

7) Environmental IP applications

7-1) Permeability estimation

SIP measurements depend on the pore-space geometry and the microstructure of the internal

rock boundary layer. For this reason, they contain information about rock permeability and

fluid properties in the pore space. The Kozeny-Carman (K-C) permeability model forms the

basis of many permeability prediction equations (e.g. Lesmes and Friedman, 2005):

2

p

sFS

aK (19)

where a is a tube shape factor, F is formation factor and Sp is specific surface area (total

mineral surface area per unit pore volume or surface area-to-porosity ratio). This equation is

useful since parameters F and Sp are often measured. The other permeability prediction

method is the Hazen model:

b

s CdK 10 (20)

where the effective grain size d10 (in cm) corresponds to the grain size for which 10% of the

sample is finer, C depends upon grain sorting and b depends upon soil texture. The Hazen

model is applicable to sediments where d10 ranges between 0.1 and 0.3 mm. Börner and Schön

38

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(1991) established the linear relationship between the quadrature component of electrical

conductivity ( ) and the specific surface area (Sp) of sandstones at a frequency of 1 Hz

(Figure 23):

)( Hz1p constS (21)

where Sp is in m-1

, Hz1 is in S/m and const=10-11

S-1

. Using this relationship in a modified

Kozeny-Carman type model, they obtained the following expression for hydraulic

conductivity:

c

Hz

c

p

s

F

a

FS

aK

1

510 (22)

where Ks is in m/s. Application of the fractal-based PARIS model of Pape et al. (1982) to a

range of rock types results in estimates of a as 10-5

and c as ranging between 2.8 and 4.6.

The constant phase angle (CPA) model of conductivity forms the basis for applying the

Börner and Schön (1991) algorithm. The formation factor F is obtained from the separated

volume conductivity ’. Börner et al. (1996) used the SIP method to estimate hydraulic

conductivity in the field, e.g. estimates of Sp in unconsolidated sands and gravels. De Lima

and Niwas (2000) also adopted a Kozeny-Carman type of petrophysical model linking IP to

hydraulic conductivity in shaly sandstones. They defined a “lithoporosity factor” which

accounts for the clay content, porosity and hydraulic tortuosity by using parameters derived

from geoelectrical measurements.

10-1

100

101

102

Sp (1/ m)

0.001

0.01

0.1

1

"(m

S/m

)

Figure 23: Linear correlation between imaginary conductivity of saturation sandstone samples

and the specific surface area (in log-log scale). The samples are saturated with 0.01 M NaCl

and measured at a frequency of 1 Hz (Börner and Schön, 1991).

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Slater and Lesmes (2002b) measured the complex conductivity response and hydraulic

properties of sandy-clay mixtures and glacial tills. On the basis of electrical measurements in

a set of samples with a hydraulic conductivity magnitude range of five orders, they

demonstrated limitations in the practical application of the Börner model and proposed a

simpler model using grain size (an easier measurement to obtain than Sp for model calibration

purposes), based on a Hazen-type empirical model. They observed a power law relationship

between Sp and Hz1 :

p

HzpS )(2000 1 (23)

where 2.05.0p %)95,53.0( 2 CIR . In their samples, however, they found that was

better correlated with effective grain size d10 (Figure 24):

b

Hz d101 0005.0 (24)

where d10 is in m, is in S/m and 1.00.1b %)95,83.0( 2 CIR . Using a Hazen type

of grain permeability model, they obtained the following expression for hydraulic

conductivity in terms of :

b

Hzs CK )( 1 (25)

where 1200800C and 2.01.1b ( is in S/m, Ks in m/s, R2=0.7).

Binley et al. (2005) examined the spectral IP response of samples taken from a UK

sandstone aquifer and compared measured parameters with physical and hydraulic properties.

They showed:

- the Cole-Cole mean relaxation time to be a more appropriate measure of IP response

than imaginary conductivity for these sediments;

- the clear link between Cole-Cole relaxation time and some measure of hydraulic

length scale (e.g. pore-throat size);

- the significant linear log-log correlation between Cole-Cole relaxation time and

hydraulic conductivity (Figure 25).

However, they did not observe the linear relationship between imaginary conductivity, ,

and Sp (Figure 26) that was demonstrated by Börner and Schön (1991). These results confirm

the validity of capillary models.

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10-4

10-2

100

d10 (mm)

0.001

0.01

0.1

1

10

100

" (

S/c

m)

Silts and Sands

Tills

Figure 24: Imaginary conductivity of unconsolidated sand samples plotted as a function of the

effective grain size d10 (modified from Slater and Lesmes, 2002b). Complex conductivity is

measured at 1 Hz and the samples are saturated with 0.01 M NaCl.

Figure 25: Variation in Cole-Cole model relaxation time, , with vertical hydraulic

conductivity, K (Binley et al., 2005).

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Figure 26: Variation in IP parameters with surface area per unit pore volume, Sp. (a)

Imaginary electrical conductivity at 1.4 Hz, ; (b) C-C model relaxation time, (Binley et

al., 2005).

The abovementioned studies showed that:

- various spectral IP parameters can be used to estimate hydraulic conductivity but it is

unclear how universally they may be applied;

- consolidated rocks may display a distinct peak in the phase of the conductivity spectra

whereas the constant phase angle model (CPA) is valid for unconsolidated sediments;

- normalized IP parameters such as the imaginary part can vary with solution

chemistry, thereby complicating the predictive relationships between IP parameters

and the desired lithologic variables.

42

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7-2) SIP measurement in vadose zone

Induced polarization studies are often used in saturated media. The first IP study to investigate

the degree of water saturation was by Vinegar and Waxman (1984). They measured the

complex conductivity responses of their samples as a function of water/oil saturation.

Waxman and Smits (1968) also studied the effects of water saturation, S, on the electrical

conductivity of oil-bearing shaly sandstone. They proposed the equation:

SBQF

Svw

d

eff / (26)

where d is the saturation index for the real conductivity. The surface conductivity term

SBQv / increases with decreasing saturation, a phenomenon that Waxman and Smits

attributed to an increase in the volume concentration of clay exchange cations at low

saturation. Imaginary conductivity therefore depended upon saturation q

sat SS , where

sat is the imaginary conductivity of the fully saturated sample and the exponent q given by

1dq where d is the saturation index for the real conductivity. Then:

v

d

vw

d

eff QnF

SiSBQ

F

S

./

1

(27)

Ulrich and Slater (2004) reported the results of laboratory IP measurements on sandy

unconsolidated samples as a function of water content and saturation history. They showed

that IP parameters (phase shift and ”) evolve with water saturation and demonstrated the

existence of hysteresis in terms of both electrolytic conduction and polarization. They also

observed that polarization is only weakly frequency-dependent over the measurement range

they used (0.1–1000 Hz). Titov et al. (2004) confirmed these results and proposed an IP

model for unsaturated sands. Their model is able to detect the critical water saturation which

corresponds to the change in pore-water geometry from bulk water to an adsorbed film

existing on the quartz grains.

Binley et al. (2005) showed a relationship between relaxation time with the Cole-Cole model

and dominant pore-throat size, and they postulated a parallel relationship between spectral IP

behavior and unsaturated hydraulic characteristics. They showed that relaxation time is

affected by the degree of fluid saturation (Figure 27). However, in agreement with Binley et

al. (2005), we think that saturation levels must be taken into account if the SIP method is to be

applied in vadose zone studies.

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Figure 27: Variation in Cole-Cole model relaxation time with saturation for core sandstone

samples VEC7-5 and VEC16-1 (Binley et al., 2005).

7-3) Detection of contaminations in vadose zone and in ground water

7-3-1) Organic contamination of ground water

During recent decades, a wide range of complex organic wastes have entered the urban

environment. A serious risk to groundwater quality has arisen from accidental spillage or

leakage from petroleum tanks and pipelines. Some of these substances are water-soluble but

many are only slightly soluble. The latter are referred to as non-aqueous phase liquids (or

NAPLs) and are divided into light and dense NAPLs according to whether they are less dense

or denser than water.

Light NAPLs are mainly petroleum products while the dense varieties include the chlorinated

hydrocarbons widely used as industrial solvents. Concentrations of these compounds

authorized in drinking water are in the parts per billion range. As NAPLs are only slightly

soluble and highly mobile, assessing their concentrations over time and their subsurface

distribution can be extremely difficult, particularly in complex environments (Cassidy, 2004).

As the NAPL moves down through the unsaturated zone, it also spreads laterally, because

capillary forces as well as gravity control its migration. Progress may be much more rapid in

fractured rocks with the contaminant following the most permeable route. Pollution of an

aquifer by NAPLs can increase by slow dissolution in groundwater. Because of the slow rate

of dissolution, NAPLs can persist as a source of pollution for decades. Light NAPLs are more

easily controlled as they float on the water table and occur at relatively shallow depths (Figure

28a). On the other hand, dense NAPLs move under the influence of their density and can

penetrate to considerable depths (Figure 28b) (Fetter, 1993).

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(a)

(b)

Figure 28: Pollution of aquifers by solvents: (a) a light NAPL (Delage, 2005) and (b) a dense

NAPL. Pollutant dissolved in groundwater is migrating through the aquifer in the direction of

groundwater flow.

Groundwater scientists and engineers have developed a number of techniques for containing

and remediating soil and ground water contamination. In general, the remediation of a site

45

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must address two issues (Fetter, 1993). If there is an ongoing source of contamination, source

control will be necessary to prevent the continuing release of contaminants to the subsurface

or from the subsurface to ground water. The second aspect of remediation is the treatment of

contaminated ground water and/or soil to remove or greatly reduce the concentrations of the

contaminants (e.g., pumping treat systems, bioremediation).

7-3-2) Contamination and SIP studies

As all polarization mechanisms show, the surface properties of solid mineral grains and

adsorption are very important to the IP effect. Take, for example, the polarization that may be

produced by membrane zones in clay materials (Marshall and Madden, 1959). When

contaminants enter the rock matrix, surface reactions between the grain surface and surface-

reactive contaminant solute affect the grain surface electrical characteristics of the soils and

rocks. Such surface reactions include:

- Adsorption (solute sticks to a solid surface by physical or chemical means and solute

diffuses into the sediment). Groundwater adsorption is a very important and common

sorptive process (Drever, 1997). For example, the dissolved components of aromatic

and chlorinated hydrocarbons, which are usually hydrophobic, are strongly adsorbed

by the solid phases in the subsurface. The resulting adsorption, which is usually

hydrophobic-driven, has been recognized as probably the most important mechanism

for groundwater contaminant removal of aromatic and chlorinated substances.

- Ion exchange (attraction between ions in the pore fluid and clay minerals in the soil).

It is very common for natural rock minerals, including clay, to be coated by organic

matter, which often has a high ion exchange capacity (Jenne, 1977).

- Chemisorption (solute is incorporated in the structure of a sediment/rock).

These processes tend to remove the contaminants from the free phase in the soil and are

affected by the saturation of the soil (Sogade et al., 2006).

The link between the IP response and adsorbed species has been recognized since the studies

of Olhoeft (1985 and 1986) and Olhoeft and King (1991). They catalogued many of these

effects and show that oxidation-reduction reactions, ion-exchange reactions, and clay-organic

solvent interaction can be distinguished from one another and from the properties of

chemically inert rocks. Olhoeft and King (1991) illustrate the ability of complex resistivity to

identify and track the extent of pollution by organic compounds. Figure 29 shows complex

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resistivity measurements of uncontaminated soil as compared to the same soil contaminated

with various organic compounds, including petrochemical wastes and oil-field brines. The

samples come from two separate wells at the waste disposal facility in Louisiana. The

uncontaminated sample shows relatively little frequency dependence in both magnitude and

phase. There is a large anomaly in phase angle for the contaminated sample centered around a

frequency of 100 Hz, indicating a strong chemically-reacting mixture. In subsequent

laboratory measurements, contaminants were added to samples with clays. Olhoeft suggested

that the IP effects were due to the polymerization of toluene to bibenzyl in the Lewis Acid

environment on the surface of montmorillonite. In effect, the low frequency is affected by a

process whereby organic molecules coat the surfaces of clay particles, inhibiting the cation-

exchange process.

4

5

6

7

8

9

(m

)

Contaminated

Uncontaminated

10-3

100

103

106

Frequency (Hz)

0

1

2

3

log

(ph

as

e-m

rad

)

Contaminated

Uncontaminated

Figure 29: Complex resistivity laboratory measurements for core samples at the waste

disposal facility in Louisiana (modified from Olhoeft and King, 1991). Measurements from

two separate wells of uncontaminated soil as compared to the same soil contaminated with

various organic compounds, including petrochemical wastes and oil-field brines.

Ward (1990) suggested that contamination would affect the effective length of the EDL. If

contamination increases the length of the EDL, then the membrane effect is more prominent

in contaminated areas and can lead to enhanced polarization. Börner et al. (1993) performed

experiments on a range of organic pollutants. They found that while the presence of

contaminants could be detected, the effects were much more subtle. A range of contaminants

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in a single clay-rich sample mixture tended to result in only simple level shifts or slope

changes in the real and imaginary parts of the resistivity (Figure 30).

10-3

10-2

10-1

100

101

102

103

Frequency (Hz)

10-6

10-5

10-4

10-3

10-2

Co

mp

lex

co

nd

ucti

vit

y (

S/m

)

Clean

Oil

hexane

Benzene

Dichlormeth.

Imaginary Conductivity

Real Conductivity

Figure 30: Frequency dependence of the real and imaginary parts of complex conductivity.

Shaly sandstone sample prepared with different organic contaminants ( water=0.01 S/m)

(Börner et al. 1993).

Sites contaminated with DNAPLs, especially the chlorinated solvents such as

perchloroethylene (PCE) and tetrachloroethylene (TCE), are often amongst the most common

and the most difficult to characterize. Ramirez et al. (1996) tried to produce images of

pollution location by combining electrical resistance tomography and complex resistivity. The

tomograms are taken at only two fixed frequencies (1 Hz and 64 Hz). they had only limited

success at producing meaningful images of a controlled release of PCE. Vanhala et al. (1992)

and Vanhala (1997b) measured complex resistivity in both the laboratory and field in an

attempt to map oil contamination in glacial till with a very low clay mineral content. They

found measurable differences between contaminated and uncontaminated experiments in both

settings. Laboratory and field results on the same materials were similar in only a qualitative

sense. They also observed a major time dependence of the signals in polluted samples,

whereas measurements in uncontaminated samples were stable. They suggested that time

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dependence alone could be an indicator of pollution. Vanhala (1997b) also investigated the

amplitude and phase (IP effect) decrease in complex resistivity after oil contamination of till

and sand samples. Resistivity increased until an oil content of 10% by volume was reached.

He explained the increase in amplitude by the fact that oil can detach ions from the surface of

rocks, thereby increasing the number of totally dissolved solids. The ion concentration in the

electrolyte increased and the thickness of EDL decreased. In some artificially contaminated

samples and gravel and sand samples from waste sites, he also observed that the phase shift

increased with prolonged maturation time.

Despite the studies mentioned in this section, however, the bio-physicochemical interactions

that impact the polarization behavior of in-situ contaminated rocks/soils have not been

investigated to date.

7-3-3) SIP studies of the effects of microbial processes

7-3-3-1) Effects of Microbial Processes

Microbe distribution in the near subsurface environment varies and is closely related to

substrate (soil, rock), water and nutrient (organic matter such as humic and fulvic acids,

organic debris) availability. Owing to the abundance and diversity of organic matter, the soil

zone has large numbers of microorganisms ranging from 106 to 10

9 organisms per gram of

soil for bacteria and 104 to 10

6 organisms per gram of soil for fungi (Balkwill and Boon,

1997). Microbial population numbers decline with depth below the soil zone, thereby

mirroring the decrease in organic matter with increasing depth. Given the low amount of

organic carbon substrate in the lower unsaturated and saturated zone, most of the microbes are

dormant, although they are viable. This viable population can quickly adapt and grow with the

introduction of organic carbon substrate and nutrients. Increasing the supply of nutrients or

organic carbon substrate stimulates the growth of microbes (Fetter, 1993).

Figure 31 shows a schematic representation of bio-physicochemical changes induced in the

subsurface environments by microbes (Atekwana et al., 2006). Microbes provided with an

organic carbon source and nutrients will grow, proliferate and develop biofilms (Figure 32).

Biofilms are organized microbial systems consisting of microbial cells, microbial by-

products, nutrients, substrates and solid surfaces. Biofilms grow on the surfaces of the

substrate and between pore openings in rocks and sediments which induce:

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- Physical changes in the rock environment. During microbial growth and biofilm

formation, the pore environment is altered in many ways, as shown in Figure 33.

Physical modifications include sediment texture, pore size, pore shape and grain

surface roughness. Biofilm growth has been found to reduce significantly the porosity

and permeability of porous media. This increased biofilm production alters pore-throat

geometry.

- Chemical changes in the rock environment. The chemistry of the fluid within the

pores where microbial growth occurs is significantly different compared to that of the

fluid in pores where microbial growth is absent. For example, the pH of the pore fluid

decreases as the carbon dioxide dissolves to form carbonic acid. Carbonic acid and

organic acids enhance the dissolution of sedimentary minerals. In addition, some of

the metabolic byproducts such as carbon dioxide and organic acids chemically interact

with the rock or sediment matrix, further altering the chemistry of the pore fluid. The

bio-chemical weathering processes in subsurface sediments potentially induce

physical changes (e.g., formation factor, tortuosity and pore geometry) in the

subsurface environment.

- Direct changes in electrical properties of the rock environment. Microbial adhesion

to mineral surfaces affects electrical interactions between the mineral particles and the

microbial cell surfaces (Figure 34). The important parameters that govern microbial

cell attachment to mineral surfaces are electrostatic attraction, hydrophobic interaction

and Van der Waals forces. This attachment of microbes to surfaces of clays alters the

EDL. Since the EDLs of microbes and clays repel each other, the thinner the EDL

layers, the less the repulsion between the clays and the cell surfaces.

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Figure 31: schematic representation of microbial-mineral interactions and how the resulting

changes in the subsurface environment impact different geophysical responses (Atekwana et

al., 2006).

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Figure 32: schematic representation of biofilm development and attachment to substrate

(Atekwana et al., 2006).

Figure 33: schematic representation of how changes in microbial growth and proliferation

impact pore structure (Atekwana et al., 2006).

Figure 34: Schematic representation of microbial interactions with clay surfaces and

attachment to clay surfaces through cation bridging (Atekwana et al., 2006).

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7-3-3-2) SIP laboratory studies of the effects of microbial processes

Sauck (2000) attributes the higher bulk electrical conductivity at hydrocarbon-contaminated

sites to biodegradation. At the time of Sauck’s (2000) study, there were no controlled studies

showing that higher conductivity resulted from biodegradation and that microbial degradation

in hydrocarbon-contaminated sediments actually caused increases in bulk electrical

properties. However, the laboratory experiments of Cassidy et al. (2001) showed a direct

relationship between the aerobic microbial mineralization of a petroleum hydrocarbon and an

increase in pore water conductivity and volatile organic acids. Atekwana et al. (2004) used DC

resistivity to investigate changes in electrical conductivity during biodegradation in a column

experiment to simulate a water saturated zone, a transition zone and a vadose zone. They

demonstrated that the microbes degraded the diesel fuel (LNAPL) in the contaminated column.

Abdel Aal et al. (2004) used the SIP method to measure the effects of microbial processes on

sediments in laboratory sand columns. The column treatments included a biotic column

(containing mineral nutrients, diesel fuel and bacteria) and two abiotic columns with one

containing only nutrients and the other containing nutrients and diesel fuel. Microbes affected

both the electrolytic and interface properties of unconsolidated sediments contaminated with

diesel (LNAPL). After a sufficient delay (about 4 months) for the microbial activity to

become effective, an increase in polarization response (imaginary conductivity) was found in

contaminated areas with microbial presence whereas none was found in the contaminated

areas without microbes (Figure 35). This increase was thought to be due either to the biofilms

formed by the bacteria because of their large surface area or to the byproducts of redox

activities.

Figure 35: Percent change in real ( ’) and imaginary ( ’’) conductivity in biotic and abiotic

sands columns over time (Abdel Aal et al., 2004).

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Ntarlagiannis et al. (2005a) measured the low frequency electrical signature of a microbial-

mediated metal sulfide precipitation process occurring in sand columns packed with Ottawa II

sand for a period of 70 days under anaerobic conditions. Nutrients (lactate and sulfate) and a

metal solution consisting of iron and zinc were introduced into the columns. Biostimulation

resulted in the precipitation of Fe and Zn sulfide. Polarization anomalies were coincident with

regions of lactate consumption, metal reduction and higher microbial population numbers.

This study demonstrates the potential for using IP parameters to monitor microbial-induced

mineral precipitation. Subsequently, Ntarlagiannis et al. (2005b) detected the presence of

microbial cells in sand columns using the SIP method. A high concentration of bacterial cells

in the sand column resulted in a higher imaginary conductivity response when compared to

sand control columns with no bacteria. They suggested that the higher imaginary conductivity

response in the bacteria columns was due to the higher total available surface area and to

alterations in the EDL of mineral grains and bacteria cells.

Davis et al. (2006) used complex conductivity measurements (0.1-1000 Hz) in biostimulated

sand-packed columns to investigate the effect of microbial growth and biofilm formation on

the electrical properties of porous media. They proposed that the observed polarization

(imaginary conductivity) response arose from the direct interaction of the attachment of

microbial cells and biofilm development on mineral grain surfaces (sand surfaces). They did

not observe any discernible relationship between microbial cell concentration and the real

conductivity component.

However, these promising studies showed that the SIP method could discriminate between the

relative contributions of microbial activity to changes in the pore fluid chemistry and changes

in the physical and chemical properties at interfaces.

7-3-3-3) SIP field studies of the effects of microbial processes

Abdel Aal et al. (2006) investigated the effects of microbial activity on IP measurements (0.1

to 1000 Hz) obtained from field samples. The measurements were acquired on sediment cores

retrieved from an aged-hydrocarbon contaminated site where intrinsic biodegradation was

occurring. In general, they recorded higher real and imaginary conductivity for samples

obtained from the contaminated locations compared to uncontaminated locations (Figure 36a).

As expected, the imaginary conductivity of the sediments at the latter was higher in the

saturated zone compared to the unsaturated zone (Figure 36b). The imaginary conductivity

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values for samples from residual phase hydrocarbon was higher compared to values obtained

for samples contaminated with dissolved phase hydrocarbons below the water table.

Figure 36: induced polarization data obtained on core samples from a hydrocarbon

contaminated site: (a) real ( ’) and imaginary ( ’’) conductivity and (b) bar plots 1 Hz

imaginary conductivity (Atekwana et al., 2006).

The real conductivity did not show a strong correlation with contamination but the imaginary

conductivity was able to better distinguish between contaminated and uncontaminated

samples. They suggested that the high imaginary conductivity response was due to an increase

in the ionic strength of the pore fluid and to an increase in the surface area of the mineral

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surfaces. These increases were attributed to the attachment of microbes which were enhanced

due to mineral weathering from metabolic byproducts such as organic and carbonic acids.

8) Conclusion

In this part, we summarize the SIP method in terms of IP models and SIP applications. In the

IP models section, the various empirical and physical models of IP were presented and

explained. The physical models based on electrochemical phenomena (EDL) usually contain

numerous parameters that reduce their potential applications. On the otehr hand, the

interfacial models are simpler to use. However, all these types of models tend to oversimplify

the real medium and they are also often derived from the literature on colloid science. In the

SIP literature, empirical models such as the constant phase angle (CPA) and Cole-Cole

models are widely used for 1D to 3D SIP modeling. In the part concerning environmental IP

applications, we presented two applications of the SIP method. Laboratory studies show that

SIP measurements depend on the pore-space geometry and the microstructure of the internal

rock boundary layer. These measurements can be used to determine the permeability and fluid

properties in the pore space in saturated samples of sandy unconsolidated sediments and

sandstones. The dependence of SIP parameters (e.g. imaginary conductivity, relaxation time)

on structural parameters (e.g. pore-throat size) led to the prediction of hydraulic conductivity

using SIP measurements, but it is unclear how universally they may be applied. When

contaminants enter the rock matrix, surface reactions between the rock and soil grain surface

and surface reactive contaminant solute (adsorption, ion exchange and chemisorption) affect

the grain surface electrical characteristics of the rock and soils.

Microbes provided with an organic carbon source and nutrients will grow, proliferate and

develop biofilms. During microbial growth, consumption of the carbon substrate, utilization

of nutrients, and the production of byproducts considerably alter the chemistry of the pore

fluids. In addition, some of the metabolic byproducts such as carbon dioxide and organic

acids chemically interact with the rock or sediment matrix, further modifying the chemistry of

the pore fluid. Hence, these physicochemical and bio-physicochemical factors alter the grain

surface electrical properties of rock and soils, and it is thought that SIP measurements would

be a powerful geophysical method to detect organic contamination in the vadose zone and in

aquifers.

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Upscaling from laboratory experiments with the SIP method to large-scale field investigations

is now a major challenge.

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Chapter 2: Papers

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Bayesian inference of the Cole-Cole parameters from time and frequency

domain induced polarization

A. Ghorbani*, C. Camerlynck

*, N. Florsch

*, P. Cosenza

* and A. Revil

**

* UMR 7619 « Sisyphe », Université Pierre et Marie Curie, Paris, France.

**CNRS-CEREGE, Université d’Aix-Marseille III, Aix-en-Provence, France.

Summary. Inverting induced polarisation (IP) parameters is important to characterize the

frequency electrical response of porous rocks. A Bayesian approach is developed to invert

these parameters assuming the electrical response is described by a Cole-Cole model in the

time or in the frequency domains. We show that the Bayesian approach provides a better

analysis of the uncertainty associated with the parameters of the Cole-Cole model by

comparison with more conventional methods based on the minimization of a cost function

using the least-square criteria. This is due to the strong non-linearity of the inverse problem

and non-uniqueness of the solution in the time domain. The Bayesian approach consists in

propagating the information provided by the measurements through the model, and to

combine this information with an a priori knowledge of the data. Our analysis demonstrates

that the uncertainty in estimating the Cole-Cole model parameters from IP data is much

higher when the measurements are performed in the time domain than in the frequency

domain. Our conclusion is that it is very difficult, if not impossible, to retrieve the correct

value of the Cole-Cole parameters from time-domain IP data using standard least-squares

methods. At the opposite, the Cole-Cole parameters can be more correctly inverted in the

frequency domain. These results are also valid for other models describing the IP spectral

response like the Cole-Davidson or power law models.

Running title: Bayesian Inference of IP Parameters

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1. Introduction

When a constant electrical current is injected through a water-saturated porous rock or

at the ground surface of a porous soil, part of the electrical power is stored in the medium.

When the current is stopped, this stored energy dissipates. This dissipation can be followed by

monitoring the voltage through the core sample or at the ground surface of the Earth

preferentially using non-polarizing electrodes (e.g., Schlumberger, 1920; Seigel, 1959). This

voltage exhibits a typical relaxation with a mean relaxation time ranging usually from few

milliseconds to thousands of seconds (e.g., Seigel et al., 1997). This phenomenon is called

“induced polarization” (abbreviated by IP hereinafter) and can be also observed in the

frequency domain. In the frequency domain, IP is characterized by a phase shift between the

injected current and the measured voltage. In the frequency domain, the apparent conductivity

of the porous material is therefore written as a complex number *( ),

)(")(')(*

1)(* i , (1)

where *( ) is the complex resistivity of the material, is the frequency of the excitation

current, i2 = -1, and ’ and ” are the measured real and imaginary components of the

conductivity, respectively.

Historically, induced polarization has been extensively used to locate ore deposits

(e.g., Madden and Cantwell, 1967). More recently, it has been applied in hydrogeophysics

(e.g., Kemna et al., 1999, Kemna et al., 2004). For example, in the case of water-saturated

sedimentary and granular materials and soils, the Cole-Cole parameters are closely related to

the grain size distribution and mean grain size of the medium (see Chelidze et al., 1977;

Chelidze and Guéguen, 1999; Kemna, 2000). Therefore, a 3D estimation of the grain size

distribution is possible using inversion of the induced polarization data obtained with an array

on non-polarizing electrodes. It was also found that the mean relaxation time of induced

polarization is also closely related to the specific surface area of the porous medium. When

combined with the electrical formation factor, the mean relaxation time can be used to

determine the hydraulic conductivity of soils and rocks (Schön, 1996; Slater and Lesmes,

2002). This opens exciting perspectives in determining non-invasively the distribution of the

hydraulic conductivity of aquifers with numerous potential applications in the domain of

water resources. The Cole-Cole function has also being used recently to model the

deformation, in the time domain, of porous sandstones (Revil et al., 2006).

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The simplest model to represent IP phenomena is the Debye model, that is

characterized by a single relaxation time. However, the range of observed relaxation times of

water-saturated rocks is relatively wide. Consequently, there were many attempts to

generalize the Debye model in the literature (Wait, 1959; Dias 1972, 2000; Pelton 1977;

Pelton et al., 1978; Wong, 1979). Among the existing models, the Cole-Cole model (Cole and

Cole, 1941) is the most successful (see Taherian et al., 1990 for a statistical comparison of the

merits of different models). The Cole-Cole model can be described by the equivalent model

with resistors and capacitances (Figure 1). According to this model, the resistivity and the

conductivity of a porous rock are,

cim

)(1

111)(* 0 , (2)

)1()(1

)(1)(* 0

mi

im

c

c

, (3)

respectively. The Cole-Cole model depends on four fundamental parameters. They are the

DC-resistivity 00 /1 ( 0 is the DC-conductivity), the chargeability m, the mean

relaxation time , and the Cole-Cole exponent c, respectively. In mineralized rocks, generally,

m and depend on the quantity of polarizable elements and their size, respectively (Pelton et

al., 1978; Luo and Zhang, 1998). The exponent c depends on the size distribution of the

polarizable elements (Vanhala, 1997; Luo and Zhang, 1998). Klein and Sill (1982) found that

the time constants were approximately to the grain size of the glass beads. Binley et al. (2005)

showed that there is a strong relationship between Cole Cole parameters determined in the

frequency domain and the hydraulic conductivity of saturated and unsaturated sandstone

cores.

Several papers have been published in the last decade to invert the Cole-Cole

parameters both in the time and frequency domains. Examples include the works by Routh, et

al. (1998), Luo and Zhang (1998), Kemna ( 2000) and Xiang et al. (2001) just to cite few

examples. These classical methods are all based on a minimization of a cost function and the

determination of a single value for each of the four Cole-Cole parameters and, in some cases

only, an estimate of the uncertainty associated with the values of the inverted parameters. If

the inverse problem is non-linear, the solution non-unique, and if the a posteriori probability

distributions of the Cole-Cole parameters does not follow Gaussian distributions, optimization

approaches can not yield the correct result. The goal of our paper is to use a Bayesian

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approach to invert the four Cole-Cole parameters and to determine the probability densities in

estimating these parameters. The inversion is performed both in the time and in the frequency

domains to compare the merits of inverting the parameters in these two domains. Finally, we

will discuss the limitation of the least-square methods by comparison with our novel

approach.

2. The Bayesian Inference Approach

Since the formulation of the Bayesian inversion by Tarantola and Valette (1982a, b)

(see also Tarantola, 1987; Mosegaard and Tarantola, 1995; and Scales and Sneider, 1997), the

Bayes theorem has been widely used to invert geophysical or hydrogeological data for a

variety of applications. The philosophy of this approach is closely related to the notion of

“information theory”. It consists actually in propagating the “information” (or knowledge)

provided by the measurements through the involved physical law (perfectly or

probabilistically known), and to include the a priori knowledge of the model parameters. Both

the data and the model parameters are described with probability distributions. The Bayesian

approach preserves the full knowledge provided by the data combined with the physical law

and the a priori information on the data and model parameters. Therefore, it is the most

suitable method to perform the inversion of non-linear problems (Tarantola and Valette,

1982a, b).

The validity of some assumptions reduces the Bayesian method to the use of simple

equations and rules (e.g., Florsch et al., 2000; Robain et al., 2001). These assumptions are the

following. (1) All the measured data and the unknown model parameters are assumed to be

independent parameters. The law connecting the data to the model parameters is written as,

d = G( ) (4)

where d is the vector of data, is the vector of the unknown model parameters, and G the

function describing the forward problem. In our case, G is based on the Cole-Cole model used

to characterize the induced polarization problem. (2) The physical law is supposed to be exact

and therefore the probability distribution of the physical law is a Dirac function. An

alternative choice would be to consider that the Cole-Cole model is not entirely appropriate to

describe induced polarization data. In such a case, a probability density, taking for example

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the form of a Gaussian distribution, could be considered with a standard deviation reflecting

the confidence given to such a model. This standard deviation could be determined using a

large data base of IP measurements performed on a wide spectrum of frequency and

determining how well the Cole-Cole model performs to fit the data (e.g., Taherian et al.,

1990). In the following, we assume however that the Cole-Cole model is correct. (3) The

measurements are supposed to follow a Gaussian distribution. This is generally true as long as

the noise affecting the data is random and results from applying the superposition principle

(Tarantola and Valette, 1982a, b).

The a posteriori probability density function p( ) combines the information related to

the Gaussian data, the a priori probability density function of the model parameters, and the

forward model d = G( ). We consider that this probability distribution is given by (Tarantola

and Valette, 1982a, b):

xCx*.exp)()(

1

dd

T50p , (5)

where Gdx , the superscript T denotes transpose of the vector, d is a vector of N

measurements, is the vector of unknown Cole-Cole model parameters to invert, ddC is the

N x N data covariance matrix, is the a priori probability density of the model parameters,

and is the homogeneous probability measure. As p( ) is a probability density, one must

have,

1)( dp . (6)

The a priori density, , is used to incorporate an a priori knowledge in the model

parameters. This probability density could be a Gaussian distribution, a multi-modal

distribution, or any probabilistic description of the parameter. A locally uniform law (the

probability distribution is constant over an interval 21 , and vanishes elsewhere) is often

used to describe this a priori density .

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The interpretation of is more challenging, especially in the present case. It has

been introduced in the general Bayesian approach to generalize Shannon’s definition of

information entropy (Tarantola and Valette, 1982a). It represents the density probability (or

measure) a given parameter that follows naturally when no a priori knowledge about this

model parameter exists. Tarantola (2005) termed this term the “homogeneous probability

measure”.

Numerous physical parameters that are positive (like distances, volumes, densities,

electrical conductivities, absolute temperatures...) usually follow non-informative laws of the

form /a where a is constant. These types of parameters are called “Jeffrey’s

parameters” (Jeffreys, 1939). These laws show scale-invariance properties: any multiplication

or power of Jeffrey’s parameters is a Jeffrey’s parameter, and a fractal transform also

conserves their forms. Considering the four Cole-Cole parameters ( 0, m, , c), only 0 and

are Jeffrey’s parameters.

Since all the four parameters involved in the Cole-Cole model are independent, the

homogeneous probability measure of the Cole-Cole parameters vector = [ 0, m, , c]T is,

0)1()(

mm

a, (7)

Hence, the Bayesian probability distribution is,

GGmma dd dCdT 1exp)1(

0, (8)

It is not easy to plot and interpret the four parameter Bayesian probability distributions

given by Eq. (8). Instead, we compute the marginal probability density functions for one or

two parameters. This approach is fundamentally different and richer than plotting the

objective function, cmGcmG dd ,,,,,, 1 dCdT

. Indeed, it is impossible to

derive full parameter information by slicing the objective function. Marginal laws preserve

the full “probability density function” (pdf) because they involve the integration of probability

over parameters selected as integrating variables. For example, the marginal pdf integrated

with respect of 0 and c is defined by,

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dcdcmpmp 00 ,,,, . (9)

However, special attention must be paid when performing this integration. In the space

parameter, dcd 0 must be a volume dV that preserves the information within intervals of

ranges 0d and dc . Therefore any change of variables must involve the corresponding

Jacobian determinant encapsulated within the volume element. It follows that Eq. (9) is

correct (in this form) only when a constant homogeneous probability measure is used. For

instance, when considering Jeffrey’s parameters, Eq. (9) can be used only if suitable variables

are used, like s’=log(s) instead of s. Tarantola (2004) strongly recommend to use “volumetric

probabilities” instead of “probability density”. It follows that the simplest way to use

“natural” variables (those for which the homogeneous probability is constant) is to make

change of variables so that all the homogeneous probabilities become constant. Therefore, we

performed the following change of variables:

)log('

)log('

))1/(log('

000

mmmm

(10)

and c is kept unchanged. The change affecting m is explained in details in Appendix A.

Another possibility that yield the same result is to consider that the transform,

')()'('

m

mmm , (11)

is constant. (m) and ’(m’) are homogeneous probability measures of m and m’, respectively

and '/ mm represents the absolute value of the Jacobian of the transformation (Tarantola

and Valette, 1982b). Equation (11) yields a differential equation to solve and

))1/(log(' mmm is a solution of this equation. Consequently, like in electrical resistance

tomography where )log( is a better parameterization than , ))1/(log( mm is a better

parametrization than m.

The same type of approach was previously applied to chemical concentrations

(Tarantola, 2005). Indeed, a chemical concentration (mass fraction) C is comprised between 0

and 1. Consequently, this is not a Jeffrey’s parameter. A concentration parameter like iC is

the ratio between a given product mass iw with respect to the total mass M, i.e., MwC ii / .

Tarantola (2005) introduced an “eigenconcentration” (in his terminology) defined by the ratio

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)/(' iii wMwC , so that 'iC is now a Jeffrey’s parameter and aCi )'log( . We adopted a

similar point of view here. In addition, the chargeability m can be seen as a “concentration of

polarizable elements” (Pelton et al., 1978), with the case m = 0 corresponding to the absence

of polarisable elements and m = 1 corresponding to the saturation of the medium in

polarizable elements. Therefore, we point out that the chargeability m shows accumulation

effects at m = 0 and m = 1. Figure 2 shows the correspondence between the familiar m and

more meaningful parameter ))1/(log(' mmm that illustrates this accumulation effect (ill-

posed correspondence between m and m’).

In conclusions, to perform our computations, we used the parameter transform

described by Eq. (10) and the integrations required in estimating the marginal pdf can be just

obtained by summing the sampled probability laws over a regular grid.

3. Inversion in the Time Domain

3.1. The Forward Problem

In the time domain, the chargeability m is determined from the residual voltage

measured immediately after the shut-down of an infinitely long, impressed current, divided by

the observed voltage just before the shut-down of the current (Seigel et al. 1959, 1997). For

non-metallic media, m ranges between 0 and 0.1. The time constant determines the rate of

decay of the residual voltage over time. In practice, this parameter has a very broad range,

from few milliseconds to thousands of seconds. The exponent c controls the curvature of the

decaying voltage in a log-log space voltage versus time (Seigel et al., 1997).

Solving the parametric inversion problem in the time-domain requires a numerical

solution for the forward problem. Several methods can be used to compute the residual

voltage assuming a Cole-Cole model. In the time domain, the following transmitted current

cycle (I0, 0, -I0, 0), with current amplitude I0 and characteristic duration T, is used. This

transmitted current cycle may be expressed in terms of Fourier series as (Tombs, 1981),

T

tnnn

nItI

n 2sin

4

3cos

4cos

2)(

1

0 . (12)

Assuming a Cole-Cole impedance model, the voltage drop measured at a pair of electrodes is

(Tombs, 1981),

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tinn

nItV nn

n

exp)(4

3cos

4cos

2Im)(

1

0 , (13)

where Im(a) corresponds to the imaginary part of the complex parameter a and Tnn 2/

are characteristic frequencies. Note that Eq. (13) converges slowly. An alternative expression

of the potential drop V(t) can be derived by applying the Laplace transform to the Cole-Cole

equation. This leads to a series of positive or negative powers of (i ). Pelton et al. (1978)

determined the voltage response corresponding to a unit positive step of applied current. This

yields

0

0)1(

)/()1()(

n

ncn

nc

tmtV , (14)

where (x) is the Gamma function. This expression of V(t) has an extremely slow

convergence for t/ > 10 and values of c less than 1. For a better convergence, Equation (14)

can be replaced by the following expression (Hilfer, 2002),

1

1

0)1(

)/()1()(

n

ncn

nc

ctmtV . (15)

Guptasarma (1982) introduced a digital linear filter to transform the frequency-domain

response of polarized ground into the time domain. The computation is easy to perform, very

fast, and the relative error of this approach is below 1%. We used separately Eq. (15) and the

Guptasarma’s approach to perform the forward model. No differences between these two

approaches were observed.

3.2. Classical inversion in the time domain

Yuval and Oldenburg (1997) solved the parametric inverse problem by using the

approach of Guptasarma (1982). As explained above, we consider a sequence of (I0, 0, -I0, 0)

current flows. The infinite pulse train )(tS response can be represented as a sequence of step

functions, each delayed by multiples of the switching time T < 4 (T is the period of the full

waveform). This sequence is given by:

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...4

5

4

3

24)()(

TtVTtV

TtV

TtV

TtVtVtS (16)

Consequently, using the superposition principle, the forward modelling of this pulse train

response requires a superposition of the series of positive and negative step responses

(Madden and Cantwell, 1967). To accelerate the convergence of the infinite pulse train

response, we apply an alternating series by using Euler transformation (Press et al., 1992).

For conventional time-domain IP receivers, it is common to sample the decay through

a sequence of N slices or windows. The value recorded for each slice is given by (Johnson,

1984, 1990),

1

)()(

10

1

3 i

i

t

tiip

i dttVttV

M . (17)

We determine numerically the chargeability from the forward modelling approach described

above. The relaxation time curve is recorded with a minimum delay time of 20 ms; the width

of each partial window lasts at least 20 ms and 20 windows are used (Table 1). This

corresponds to classical values used for field investigations. The rate of sampling on the delay

curve is 5 ms. We note Vp the potential at the cut-off of the electrical current, that is normally

close to the initial value of the decay curve V(t). Since the chargeability is given by the

normalized ratio of )()( tdtV with respect to Vp(ti+1-ti). This ratio does not depend on 0.

Therefore, in the inversion process, we used the normalized transient potential V(t) / Vp.

When using Fourier’s series, at least 104 harmonics should be used to ensure the

convergence of the series. This involves frequencies from 0.125 Hz to 1250 Hz. However, in

order to reproduce the acquisition of data in the field, we consider a sampling rate of 5 ms like

in most field acquisitions. It is certain that this choice affects the recorded voltage signal (see

Table 1).

3.3. Bayesian Inversion in the Time Domain.

The computation of the Bayesian solution of the inverse problem is based on Eq. (8).

We note d the vector of the N sampled normalized residual voltage data supposed to be

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independent of each other while is the vector of three remaining unknown parameters (m’,

c, ’). All the a priori distributions where taken uniform on the changed variables within given

intervals. The parameter m’ is in the range -2.3 to +2.3 and consequently m, given by

)101/(10 '' mmm , is in the range 0.005 to 0.995. The parameter c is in the range 0 to 1

while log is in the range -4 to 4 or alternatively is in the range 10-4

to 104 s.

To represent the 3-D a posteriori pdfs, we use 3-D plots in the space of the model

parameters (m’, c, ’). We plot the two-by-two marginal laws in the space (m’, c), (m’, ’), and

(c, ’), respectively. To provide a good insight about the results of the inversion, we study a

set of eight examples, each of the three Cole-Cole parameters m, c, and can take two types

of distinct values, which are m = (0.2 and 0.8), c = (0.25 and 0.75), and = (0.01 and 10).

However, because some of these eight cases present similar results in terms of marginal laws

in the space (m’, c), (m’, ’), and (c, ’), we choose to present four cases exhibiting very

distinct behaviours. They are displayed on Figures 3 to 7. These results are discussed in the

following section.

3.4. Presentation of the Results

Case 1. This case corresponds to the following set of parameters (m = 0.8, c = 0.25,

and = 0.01 s). In this first case m is large but both c and are small. Figure 3 shows that the

solution crosses the entire investigated domain. The marginal plots are shown on Figures 3c

to 3e. The marginal plots are not merely slices of the full solution domain. Figure 3b provides

the marginal pdf in the ( , c) plane (after integration, the diagrams are plotted by using the

familiar parameter m instead of m’).

The “equivalence domain” shown by Figure 3c is rather complex and very far from

those that would be given by Gaussian distributions. Several remarks can be made from

Figure 3. First, one must remember that the marginal laws are built to provide probabilistic

estimations of the inverted parameters. Let us consider, for instance, Figure 3e. This Figure

shows the pdf of m and log , that we note 'mp . If this probability is properly

normalized, we have,

1',

4

4

1

0

dmdmp . (18)

It can be used to determine the following probability:

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',)',(

1

1

D

dmdmpDmp . (19)

The maximum of the pdf must be considered carefully. Indeed, considering the domains D2

and D3 of Figure 3e, it is possible that )',()',( 23 DmpDmp due to the fact that it is

the pdf integrals that are meaningful instead of the pdf themselves.

Figure 3e shows the marginal law (m’, ’) for which several maxima exist. This

explains the failure of the classical least-square methods to determine the Cole-Cole

parameters from time domain IP data. It is also important to realize that in such a case, the a

posteriori conditional pdf, when integrated within a given box, can have a maximum in a

region where the pdf has no maxima. This depends on the sharpness of the pdf in the box. We

will discuss this point below.

Case 2. This case corresponds to the following set of parameters m = 0.8, c = 0.75,

and = 10 s. In this case, the equivalence domain is simple (Figure 4). The consideration of

the values of the model parameters (m, ’, and c) following the relations between them that are

represented on these diagrams will all permit to fit the data equally well. For example, if we

take = 1000 s ( ’ = 3), m = 0.97, and c=0.6, it fits the data as well as taking m = 0.8, c =

0.75, and = 10 s.

Case 3. This case corresponds to the following set of parameters m = 0.2, c = 0.25,

and = 0.01 s. In this case, the marginal laws present an equivalence between the parameters

that is more pronounced than in the previous cases (Figure 5). For instance, there are more

than one values of for one values of m that fit the data.

Case 4. This case corresponds to the following set of parameters m = 0.2, c = 0.75,

and = 0.01 s. In the marginal law of (m, c), Figure 6d, two branches appear corresponding to

two possible solution areas. From this pdf, we can compute the marginal law of parameter c

alone, as shown on Figure 6b. It appears that the left part of the (m, c) pdf has a smaller

volume than the large “mount” on the right side of the plot, although the left part reach a

higher pdf in two or three dimensions. On Figure 6a, the pdf has a narrow shape. In such a

case, the least-square methods or the use of simulated annealing algorithms reach the absolute

maximum of the pdf in the 3-D parameter space domain but these methods would still fail in

retrieving the correct values of the model parameters. Indeed, the best fit will be found on the

left ridge, even though the initial synthetic parameter belongs to the right side of the plot (c =

0.75). This illustrates very well the suitability of the Bayesian approach for strongly non-

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linear inverse problems. There are equivalence laws like for the one exhibited by the case

corresponding to m = 0.8, c = 0.75, and = 0.01 s.

Moreover, these diagrams show that the chargeability cannot be correctly recovered.

Indeed, any value of m comprised between 0 and 1 will fit the data equally well. Catalogues

of curves used in some software to select a solution could lead to serious errors in estimating

the model parameters. Note that whatever the real value of m, inversion of the model

parameters in the time domain yields also an acceptable solution with 1m . In other words,

for any value of m, good fits of the time relaxation curve can be obtained for suitable values

of c and . Figure 6 shows for example, in connection with the set of model parameters (m =

0.2, c = 0.75, and =0.01 s, see curve a in Figure 7), the curve obtained with this set of value

and an alternative (and very different) solution with model parameters (m = 0.99, c = 0.75,

and = 0.0028 s, curve c on Figure 7). Figures 6 and 7 also show that two remote points in

the space parameter see case (a) and (c) on Figure 6, yields time responses that can not be

distinguished from each other. Moreover, as far as error bars are properly taken into account,

even case (b) can not be distinguished from cases (a) and (c). For comparison, the curve with

the fully non-compatible solution (m = 0.6, c = 0.2, and = 10 s) is also plotted (case (d) on

both figures).

4. Inversion in the Frequency Domain

Various inversion algorithms based on the non-linear, iterative, least-square method

have been proposed to invert spectral induced polarization (SIP) measurements using the

Cole-Cole model (see Pelton et al. 1978, 1984, Jaggar and Fell, 1988; Luo and Zhang 1998;

and Kemna et al., 2000). Xiang et al. (2001) proposed an alternative algorithm, called the

“direct inversion” that directly identifies the values of the Cole-Cole parameters. However,

their algorithm does not provide a full covariance analysis of the inverted values of the model

parameters. In this section, we apply the Bayesian algorithm to analyze the information that

can be retrieved from spectral induced polarization data. In addition, we compare the

uncertainties of the model parameters with those obtained in the time domain.

We first analyze the influence of the Cole-Cole parameters on the SIP response in the

frequency domain. Increasing the Cole-Cole exponent c increases both the steepness of the

phase peak and the slope of the amplitude curve response. The DC-resistivity 0 shifts the

amplitude curve vertically, and has no effect on the phase curve. The DC-resistivity is related

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to the formation factor of the sample, the conductivity of the pore fluid, and the cation

exchange capacity of the medium (e.g., Revil et al., 1998).

In the present case and accounting for the additional parameter 0, the results consist

in the evaluation of 6 marginal pdfs, one for each couple of parameters. We use the same set

of synthetic data as proposed in the previous section and we investigate the frequency range

1.43 mHz to 12 kHz with a sampling rate given by NkHz 2/12 where N is number of

frequency used in the SIP FUCHS-II equipment (Radic Research). The a priori range of the

model parameters is the same as in the time domain case investigated in section 3 except for

the additional DC-resistivity, 0. For this parameter, we consider the a priori range (30-300

m) while the real value of this parameter is 100 m for all the synthetic cases analyzed

below. Since 0 is a Jeffrey’s parameter, we use the uniform probability density:

aa

)ln(')( 0

0

0 . (20)

In the time domain, we observed that the application of the inversion scheme requires

the computation of slowly convergent series. The inversion of the Cole-Cole parameters in the

frequency domain is hopefully simpler than in the time domain. Indeed, the Cole-Cole model

given by Eqs. (2) and (3) corresponds to an analytical complex function transfer, and is

consequently easier to invert than the slowly converging series arising in the time domain.

The cases are analyzed in Figures 8 to 11. Figure 8 presents inversion of synthetic data

in the spectral domain with ( 0 = 100 m, m = 0.8, c = 0.25, and = 0.01 s). Parameters are

well determined, only m have a small uncertainty of ± 0.1. Figure 9 shows results obtained

with parameters ( 0 = 100 m, m = 0.8, c = 0.25, and = 10 s). Large equivalence laws

appear between all the parameters; for example a strong correlation does exist between the

values of ’ and 0 for instance, 0=125 m (log 0=2.1), and s are also compatible

with the synthetic data. Figure 10 presents the results for the following values of the

parameters ( 0=100 m, m = 0.8, c = 0.75, and = 0.01 s). The distribution of the model

parameters c and m are wide while and 0 can be accurately determined. There is an ill-

posed correspondence between m and ))1/(log(' mmm that’s appears in m direction.

Results for the model parameters ( 0 = 100 m, m = 0.2, c = 0.25, and = 0.01 s) are

represented on Figure 11. In this case, all the model parameters can be accurately determined.

Note that the uncertainty of c and m are however correlated.

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To finish this section, we perform a test using a set of real data. We use the data

published by Xiang et al. (2003). The results of the Bayesian analysis are shown on Figure 12.

This figure shows the marginal pdf when data are analyzed in the frequency interval (10 mHz

- 10 kHz). The space of the model parameters appears much simpler than in the time domain

(there is only one pdf maximum and the pdfs appear nearly Gaussian). Three model

parameters ( 0, m, and ) are well determined, but the Cole-Cole exponent c is poorly

determined. The maxima of the pdf obtained by the two-by-two marginal laws (the

coordinates of contour centres) are very close to the parameters derived from a classical least-

square method. So our approach validates the use of the classical least-square method in that

problem.

5. Use of Harmonics of Square Current Signals

An alternative way to perform field or laboratory measurements consists in injecting

square signal currents with different periods and to measure the associated voltage difference

using a pair of non-polarizing electrodes (e.g., Zonge Engineering and Research

Organization). In this case, the spectrum of the measured potential difference is the

superposition of the signal corresponding to each square signal. To analyze this case, we use

square current signals with the following periods 0.125, 1.0, and 8.0 seconds, respectively.

Then, we calculate the spectrum of frequencies 0.125, 1.0, and 8.0 Hz, including the 3rd, 5th,

7th, and 9th harmonics (Table 2) for each fundamental frequency that is presented in Figure

13a. The transfer function is:

)(

),()( 0

0nI

nVkn , (21)

where n is the harmonic number of each signal, 0 is the fundamental frequency, , V, and I

are the apparent resistivity, the voltage drop, and the injected current, respectively. This

function has uncertainties that increase with the number n of harmonics of the fundamental

frequency. These errors are incorporated in our Bayesian inversion approach (Figure 13b).

We assume that there is not error associated with the value of the injected current and that

there is only a constant deviation x associated with the measured potential drop. It follows

that the spectral deviation is the deviation X (Florsch et al., 1995):

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N

xX , (22)

where N is the number of point of time sequence. The standard deviation of data can be

written:

)()( 0nX . (23)

We compute the a posteriori probability density function given by Eq. (5) using the

covariance matrix associated with the data given by Eq. (23). A synthetic example for the

inversion of the model parameters is presented on Figure 14. The values of the model

parameters are ( 0 = 100 m, m = 0.2, c = 0.75, and = 0.001 s). From the results plotted on

this figure, we conclude that when harmonics of a fundamental frequency are used to perform

induced polarization, only 0 is well-determined while the uncertainties associated with the

other parameters (m, c, are still very strong.

6. Conclusion

The Bayesian approach provides the information (or probability densities) associated

with the Cole-Cole parameters determined from induced polarization measurements in the

time or frequency domains. Because the Cole-Cole parameters can be used to determine the

hydraulic conductivity of aquifers, this approach has strong implications in hydrogeophysics

to determine the permeability using a Bayesian analysis. In this paper, the Bayesian approach

has been applied to the determination of the Cole-Cole parameters from measurements

simulated both in the time domain and in the frequency domain for which a wider range of

frequencies are investigated. While the use of the Cole-Cole model could show a limitation of

our approach, we point out that the Bayesian approach developed here could be used to

investigate the uncertainty associated with the inversion of alternative models like the Cole-

Davidson model.

The Bayesian procedure results in an enlightened explanation of why the classical time

domain approach cannot lead to a proper estimate of the Cole-Cole parameters. For

completeness, we investigated the frequency domain induced polarization by using the

harmonics of square current signals in a low-frequency range, theoretically reaching a broader

spectrum than just using the classical time domain relaxation associated with a single current

injection (corresponding to a single frequency). However, we showed that error bars increase

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for the harmonics of each fundamental frequency. The Bayesian approach shows that, even in

this case, the correct estimation of the Cole-Cole parameters with the classical least-square

methods is difficult. Finally the Bayesian approach allows delineating “equivalent domains”

in the space of the model parameters accounting for the uncertainty in the measurements.

Acknowledgement. We are indebted to the INSU-ECCO program (project Polaris II, 2005-

2007) for support to this work. We thank the Referees and the Editor for their useful

comments.

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Mosegaard, K., and Tarantola, A., 1995, Monte Carlo Sampling of Solutions to Inverse

Problems, Journal of Geophysical Research, 100, 12431-12477.

Pelton, W. H., Smith, B. D., and Sill, W. R., 1984, Interpretation of complex resistivity and

dielectric data, part II, Geophys. Trans., 29(4), 11–45.

Pelton, W. H., 1977, Interpretation of Complex Resistivity and Dielectric Data, Ph.D. Thesis,

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Pelton, W. H., Ward, S. H., Hallof, P. G., Sill, W. R. and Nelson, P. H., 1978, Mineral

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Routh, P. S., Oldenburg, D. W. and Li, Y., 1998, Regularized inversion of spectral IP

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Tarantola, A., 1987, Inverse Problem Theory, Methods for Data Fitting and Model Parameter

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Tarantola, A., and Valette, B., 1982a, Generalized nonlinear inverse problems solved using

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Tarantola, A., and Valette, B., 1982b, Inverse problems - Quest for information, Journal of

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Vanhala, H., 1997, Laboratory and Field Studies of Environmental and Exploration

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Wong, J., 1979, An electrochemical model of the induced-polarization phenomenon in

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identified Cole-Cole models, Computers and Geosciences, 29, 647-654.

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Appendix A. Determination of m’

To derive the non-informative structure of m, we consider an electrical equivalent

circuit where two resistors are involved (RA and RB). In this case, the chargeability m can be

expressed as 1

/1 AB RRm (Figure 1). Since RA and RB are both Jeffrey’s parameters,

their ratio AB RRS / is also a Jeffrey’s parameter. The homogeneous probability

distribution (HPD) of m is:

)1()(

mm

am , (A1)

where a is a constant and )1,0(m . Alternatively, the chargeability can be written as,

lim

lim 00

(A2)

0

1m . (A3)

However, is not a Jeffrey’s parameter since we have necessarily 0 . However, the

HPD of the normalized chargeability,

m

mm

1*

0

, (A4)

is,

*)1(**)(

mm

am , (A5)

where a is a constant. The HPD of m* has the same form than the HPD of m.

We look for an expression for the chargeability m’ satisfying )'(m is constant. If we

write )1/(1 Sm where S is a Jeffrey’s parameter, this yield,

m

mS SS

1)( , (A6)

and,

m

mS SS

1log)(log log (A7)

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is a constant. If X is a Jeffrey’s parameter, 1 / X is also a Jeffrey’s parameter. It follows:

am

mm

1log' , (A8)

where a is a constant. Therefore the transform

m

mm

1log' , (A9)

is a suitable solution.

91

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Captions

Figure 1. An equivalent circuit model corresponding to the Cole-Cole model.

Figure 2. Ill-posed correspondence between the chargeability m of the Cole-Cole

model and its normalized version ))1/(log(' mmm used for the Bayesian inversion.

Figure 3. Time domain inversion model with m = 0.8, c = 0.25, and = 0.01 s. (a) 3-D

space of a posteriori pdf. (b) a posteriori pdf on m interval parameter while fixed ( ’) and (c)

parameters.(c), (d) and (e) Marginal a posteriori pdf of two-by-two set of parameters.

Figure 4. Time domain inversion model with m = 0.8; c = 0.75, and = 10 s. (a) 3-D

space of a posteriori PDF. (b), (c) and (d) Marginal a posteriori pdf of two-by-two parameter.

Figure 5. Time domain inversion model with m = 0.2, c = 0.25, and = 0.01 s. (a) 3-D

space of a posteriori PDF. (b), (c) and (d) Marginal a posteriori pdf two-by-two of parameters.

Figure 6. Time domain inversion model with m = 0.2, c = 0.75, and = 0.01 s. (a) 3-D

space of a posteriori pdf. (b) Marginal a posteriori pdf law of parameter c alone. (c), (d) and

(e) Marginal a posteriori pdf two-by-two of parameters.

Figure 7. Partial Chargeability curve for a, b, c and d points represented on Figure 6.

Figure 8. The Marginal pdf of the Cole-Cole parameters ( 0 = 100 m, m = 0.8, c =

0.25, and = 0.01 s) for synthetic data.

Figure 9. The Marginal pdf of the Cole-Cole parameters ( 0 = 100 m, m =0.8, c =

0.25, and = 10 s) for synthetic data.

Figure 10. The Marginal pdf of the Cole-Cole parameters ( 0 = 100 m, m = 0.8, c =

0.75, and = 0.01 s) for synthetic data.

Figure 11. The Marginal pdf of the Cole-Cole parameters ( 0 = 100 m, m = 0.2, c =

0.25, and = 0.01 s) for synthetic data.

Figure 12. Marginal pdf of the Cole-Cole parameters ( 0=22 m, m = 0.13, c = 0.69,

and = 0.001 s) for the data of Xiang et al. (2003).

Figure 13. (a) Spectrum with fundamental frequency 0.125, 1.0, and 8.0 Hz, including

the 3rd, 5th, 7th, and 9th harmonics for each fundamental frequency. (b) Spectrum of

response divided by reference and error bars for each harmonic.

Figure 14. The Marginal pdf of the Cole-Cole parameters ( 0 = 100 m, m = 0.2, c =

0.75, and = 0.001 s) for synthetic data. Spectrum is created by 0.125, 1.0, and 8.0 Hz,

including the 3rd, 5th, 7th, and 9th harmonics for each fundamental fre

92

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Tables

Table1. Number of chargeability slices and time interval sampling of decay curve in time

domain method in Cole mode of Syscal Pro® instrument. Vdly and Mdly are delay times (in

ms) from which the samples (sampling rate of 10 ms) are taken into account after injection

and after the current cut off, respectively. The period of current signal injection is 2 s.

Vdly Mdly 1 2-4 5-6 7 8 9 10 11 12 13 14 15 16 17 18 19 20

1260 20 20 30 40 50 60 70 80 90 100 110 120 130 140 150 160 180 200

Table 2. Fundamental frequencies and their harmonics used by the Zonge instrument in its

complex resistivity mode.

Harmonics Frequencies

(in Hz)

3 5 7 9

0.125 0.375 0.625 0.875 1.125

1 3 5 7 9

8 24 40 56 72

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Figures

Figure 1

0 0.2 0.4 0.6 0.8 1m

-3

-2

-1

0

1

2

3

Log(m/(1-m))

Figure 2

(i x)-c

Ra

Rb

94

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0 0.2 0.4 0.6 0.8 1m

0

0.2

0.4

0.6

0.8

1

PDF(m/c,log())

-4 -3 -2 -1 0 1 2 3 4log( )

0

0.1

0.2

0.3

0.4

0.5

0.6

0.7

0.8

0.9

1

c

0 0.1 0.2 0.3 0.4 0.5 0.6 0.7 0.8 0.9 1c

0.1

0.2

0.3

0.4

0.5

0.6

0.7

0.8

0.9

m

-4 -3 -2 -1 0 1 2 3 4log( )

0.1

0.2

0.3

0.4

0.5

0.6

0.7

0.8

0.9

m

Figure 3

D2

D3

D1

m=0.8

c=0.25

=0.01 sec

(a) (b)

(c) (d) (e)

95

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-4 -3 -2 -1 0 1 2 3 4log( )

0

0.1

0.2

0.3

0.4

0.5

0.6

0.7

0.8

0.9

1

c

0 0.1 0.2 0.3 0.4 0.5 0.6 0.7 0.8 0.9 1c

0.1

0.2

0.3

0.4

0.5

0.6

0.7

0.8

0.9

m

-4 -3 -2 -1 0 1 2 3 4log( )

0.1

0.2

0.3

0.4

0.5

0.6

0.7

0.8

0.9

m

Figure 4

m=0.8

c=0.75

=10 sec

(a)

(b) (c) (d)

96

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-4 -3 -2 -1 0 1 2 3 4log( )

0

0.1

0.2

0.3

0.4

0.5

0.6

0.7

0.8

0.9

1

c

0 0.1 0.2 0.3 0.4 0.5 0.6 0.7 0.8 0.9 1c

0.1

0.2

0.3

0.4

0.5

0.6

0.7

0.8

0.9

m

-4 -3 -2 -1 0 1 2 3 4log( )

0.1

0.2

0.3

0.4

0.5

0.6

0.7

0.8

0.9

m

Figure 5

m=0.2

c=0.25

=0.01 sec

(a)

(b) (c) (d)

97

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0 0.2 0.4 0.6 0.8 1c

0

0.2

0.4

0.6

0.8

1

PDF(c)

-4 -3 -2 -1 0 1 2 3 4log( )

0

0.1

0.2

0.3

0.4

0.5

0.6

0.7

0.8

0.9

1

c

0 0.1 0.2 0.3 0.4 0.5 0.6 0.7 0.8 0.9 1c

0.1

0.2

0.3

0.4

0.5

0.6

0.7

0.8

0.9

m

-4 -3 -2 -1 0 1 2 3 4log( )

0.1

0.2

0.3

0.4

0.5

0.6

0.7

0.8

0.9

m

Figure 6

(a) (b)

m=0.2

c=0.75

=0.01 sec

(c) (d) (e)

ac

b

d a

c

b

d

a

c

b

d

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0 0.4 0.8 1.2 1.6 2time (sec)

0

0.05

0.1

0.15

0.2

0.25P

art

ial C

harg

eabili

tya (m=0.2 c=0.75 =0.01sec)

b (m=0.04 c=0.86 =0.005 sec)

c (m=0.99 c=0.75 =0.0028 sec)

d (m=0.6 c=0.2 =10 sec)

ba

c

d

Figure 7

99

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-4 -3 -2 -1 0 1 2 3 4log( )

0

0.1

0.2

0.3

0.4

0.5

0.6

0.7

0.8

0.9

1

c

0 0.1 0.2 0.3 0.4 0.5 0.6 0.7 0.8 0.9 1c

1.5

1.6

1.7

1.8

1.9

2

2.1

2.2

2.3

2.4

2.5

log(

)

-4 -3 -2 -1 0 1 2 3 4log( )

1.5

1.6

1.7

1.8

1.9

2

2.1

2.2

2.3

2.4

2.5

log(

)

0 0.1 0.2 0.3 0.4 0.5 0.6 0.7 0.8 0.9 1c

0.1

0.2

0.3

0.4

0.5

0.6

0.7

0.8

0.9

m

-4 -3 -2 -1 0 1 2 3 4log( )

0.1

0.2

0.3

0.4

0.5

0.6

0.7

0.8

0.9

m

0.1 0.2 0.3 0.4 0.5 0.6 0.7 0.8 0.9m

1.5

1.6

1.7

1.8

1.9

2

2.1

2.2

2.3

2.4

2.5

log(

)

Figure 8

0=100 m

m=0.8

c=0.25

=0.01 sec

100

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-4 -3 -2 -1 0 1 2 3 4log( )

0

0.1

0.2

0.3

0.4

0.5

0.6

0.7

0.8

0.9

1

c

0 0.1 0.2 0.3 0.4 0.5 0.6 0.7 0.8 0.9 1c

0.1

0.2

0.3

0.4

0.5

0.6

0.7

0.8

0.9

m

-4 -3 -2 -1 0 1 2 3 4log( )

0.1

0.2

0.3

0.4

0.5

0.6

0.7

0.8

0.9

m

0 0.1 0.2 0.3 0.4 0.5 0.6 0.7 0.8 0.9 1c

1.5

1.6

1.7

1.8

1.9

2

2.1

2.2

2.3

2.4

2.5

log

()

0.1 0.2 0.3 0.4 0.5 0.6 0.7 0.8 0.9m

1.5

1.6

1.7

1.8

1.9

2

2.1

2.2

2.3

2.4

2.5

log(

)

-4 -3 -2 -1 0 1 2 3 4log( )

1.5

1.6

1.7

1.8

1.9

2

2.1

2.2

2.3

2.4

2.5

log

()

Figure 9

0=100 m

m=0.8

c=0.25

=10 sec

101

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-4 -3 -2 -1 0 1 2 3 4

log( )

0

0.1

0.2

0.3

0.4

0.5

0.6

0.7

0.8

0.9

1

c

0 0.1 0.2 0.3 0.4 0.5 0.6 0.7 0.8 0.9 1c

0.1

0.2

0.3

0.4

0.5

0.6

0.7

0.8

0.9

m

-4 -3 -2 -1 0 1 2 3 4

log( )

0.1

0.2

0.3

0.4

0.5

0.6

0.7

0.8

0.9

m

0 0.1 0.2 0.3 0.4 0.5 0.6 0.7 0.8 0.9 1c

1.5

1.6

1.7

1.8

1.9

2

2.1

2.2

2.3

2.4

2.5

log

()

0.1 0.2 0.3 0.4 0.5 0.6 0.7 0.8 0.9m

1.5

1.6

1.7

1.8

1.9

2

2.1

2.2

2.3

2.4

2.5

log(

)

-4 -3 -2 -1 0 1 2 3 4log( )

1.5

1.6

1.7

1.8

1.9

2

2.1

2.2

2.3

2.4

2.5

log(

)

Figure 10

0=100 m

m=0.8

c=0.75

=0.01 sec

102

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-4 -3 -2 -1 0 1 2 3 4log( )

0

0.1

0.2

0.3

0.4

0.5

0.6

0.7

0.8

0.9

1

c

0 0.1 0.2 0.3 0.4 0.5 0.6 0.7 0.8 0.9 1c

0.1

0.2

0.3

0.4

0.5

0.6

0.7

0.8

0.9

m

-4 -3 -2 -1 0 1 2 3 4log( )

0.1

0.2

0.3

0.4

0.5

0.6

0.7

0.8

0.9

m

0 0.1 0.2 0.3 0.4 0.5 0.6 0.7 0.8 0.9 1c

1.5

1.6

1.7

1.8

1.9

2

2.1

2.2

2.3

2.4

2.5

log(

)

0.1 0.2 0.3 0.4 0.5 0.6 0.7 0.8 0.9m

1.5

1.6

1.7

1.8

1.9

2

2.1

2.2

2.3

2.4

2.5

log(

)

-4 -3 -2 -1 0 1 2 3 4log( )

1.5

1.6

1.7

1.8

1.9

2

2.1

2.2

2.3

2.4

2.5

log(

)

Figure 11

0=100 m

m=0.2

c=0.25

=0.01 sec

103

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-4 -3 -2 -1 0 1 2 3 4log( )

0

0.1

0.2

0.3

0.4

0.5

0.6

0.7

0.8

0.9

1

c

0 0.1 0.2 0.3 0.4 0.5 0.6 0.7 0.8 0.9 1c

1.3

1.31

1.32

1.33

1.34

1.35

1.36

1.37

1.38

1.39

1.4

log

()

-4 -3 -2 -1 0 1 2 3 4log( )

1.3

1.31

1.32

1.33

1.34

1.35

1.36

1.37

1.38

1.39

1.4

log

()

0 0.1 0.2 0.3 0.4 0.5 0.6 0.7 0.8 0.9 1c

0.1

0.2

0.3

0.4

0.5

0.6

0.7

0.8

0.9

m

-4 -3 -2 -1 0 1 2 3 4log( )

0.1

0.2

0.3

0.4

0.5

0.6

0.7

0.8

0.9

m

0.1 0.2 0.3 0.4 0.5 0.6 0.7 0.8 0.9m

1.3

1.31

1.32

1.33

1.34

1.35

1.36

1.37

1.38

1.39

1.4

log

()

Figure 12

0=22 m

m=0.13

c=0.69

=0.001 sec

104

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0.1 1 10 100Frequency (Hz)

0

0.2

0.4

0.6

0.8

1

1.2

1.4

0.1 1 10 100

0

0.2

0.4

0.6

0.8

1

1.2

1.4

0.1 1 10 100

0

0.2

0.4

0.6

0.8

1

1.2

1.4A

mp

litu

de

(v)

0.1 1 10 100Frequency (Hz)

93

94

95

96

97

98

99

100

101

Resis

tivity (

m)

Figure 13

(a) (b)

105

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-4 -3 -2 -1 0 1 2 3 4log( )

0

0.1

0.2

0.3

0.4

0.5

0.6

0.7

0.8

0.9

1

c

0 0.1 0.2 0.3 0.4 0.5 0.6 0.7 0.8 0.9 1c

0.1

0.2

0.3

0.4

0.5

0.6

0.7

0.8

0.9

m

-4 -3 -2 -1 0 1 2 3 4log( )

0.1

0.2

0.3

0.4

0.5

0.6

0.7

0.8

0.9

m

0 0.1 0.2 0.3 0.4 0.5 0.6 0.7 0.8 0.9 1c

1.9

1.95

2

2.05

2.1

2.15

2.2

log

()

0.1 0.2 0.3 0.4 0.5 0.6 0.7 0.8 0.9m

1.9

1.95

2

2.05

2.1

2.15

2.2

log

()

-4 -3 -2 -1 0 1 2 3 4log( )

1.9

1.95

2

2.05

2.1

2.15

2.2

log

()

Figure 14

0=100 m

m=0. 2

c=0.75

=0.001 sec

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CR1Dinv: A Matlab program to invert 1D Spectral Induced Polarization data for Cole-Cole model include electromagnetic effects

A. Ghorbani*, C. Camerlynck*, N. Florsch*

* UMR 7619 « Sisyphe », Université Pierre et Marie Curie, Paris, France.

Abstract: An inversion code in Matlab is constructed to recover the parameters of Cole-Cole model from spectral induced polarization (SIP) data in a 1D earth. In a spectral induced polarization survey the impedances at various frequencies are recorded. Both induced polarization and electromagnetic coupling effects occur simultaneously in this frequency bandwidth, the latter being more and more dominate when frequency increases. We used CR1Dmode code published by Ingeman-Nielsen and Baumgartner (2006) as forward modeling. This code solves electromagnetic responses in the presence of complex resistivity effects in a 1D earth. A homotopy method is designed to overcome the local convergence of normal iterative methods. In addition, to further condition the inverse problem, we incorporate standard Gauss-Newton (or Quasi Newton) methods. The graphical user interfaces allows easy entering the data and the a priori model and also cable configuration. We present two synthetic examples to illustrate that the spectral parameters can be recovered from multifrequency complex resistivity data.

Keywords: Complex resistivity; Cole-Cole model; Spectral Induced Polarization; EM coupling, Homotopy inversion method.

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1. Introduction

Spectral Induced Polarization (SIP) is widely used in environmental and engineering

geophysical prospecting, as well as mineral exploration (e.g., Pelton et al., 1978, Luo and

Zhang, 1998), hydrogeophysics (e.g., Kemna et al., 1999; Kemna et al., 2004; Binley et al.,

2005), organic and non-organic contamination of soils and rocks (e.g., Vanhala, 1997, Abdel

Aal et al., 2006).

The mutual impedances of grounded wires (electromagnetic coupling between the

transmitter, the receiver and the ground) are of prime importance in SIP surveys. At low

frequencies, electromagnetic (EM) couplings and normal polarization effects of the

subsurface material have similar functional behavior with respect to the conductivity of the

earth and their combined effects are recorded in an SIP survey. EM coupling is a major

impediment in the interpretation of induced polarization (IP) data. EM coupling also increases

with the dipole length and dipole separation and with conductivity and frequency (Dey and

Morrison, 1973). For deep exploration, the dipoles and their separation must be large; hence,

the operational frequency is usually low to avoid EM coupling. Unfortunately, the natural EM

field spectrum rises steeply below 1.0 Hz enough (Gasperikova and Morrison, 2001). One

way to avoid EM coupling is measuring SIP data at frequencies low enough that any EM

coupling is either negligible or predictable (Katsube and Collett, 1973; Wynn and Zonge,

1977). Loke et al. (2006) use a regularized least-squares optimization method to recover the

SIP parameters in the 2D problem, but reduce the EM coupling phenomena by limit the

maximum frequency between 10 and 100 Hz. However, elimination of high frequency of IP

spectrum, it eliminate the important information.

Generally for Time Domain methods, one hopes and expects to avoid the problem of

EM coupling by use of the “delay time” (waiting a suitable length of time, a few tens of

milliseconds) after the transmitter is switched off before starting to acquire useful data.

During this delay it is expected that the EM coupling will varnish away to negligible levels.

However, it is not possible to avoid the problem this way in highly conductive environments.

In SIP literature, numerous approaches are to remove EM coupling effects in SIP data

(e.g., Coggon 1984; Song 1984; Pelton et al. 1978; Brown, 1985; Cao et al., 2005; Routh and

Oldenburg, 2001). However, all of these studies deal with Dipole-Dipole electrode array.

A forward modeling code has been developed that is capable of handling several

commonly used electrical and electromagnetic methods in a 1D environment by Ingeman-

Nielsen and Baumgartner (2006). This code calculates the mutual impedance in different

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frequencies of 1D ground layers for Cole-Cole model and different grounded electrode arrays.

Also, it considers the influence caused by the placement of the wires.

Generally, the liberalized inversion method is used to solve of the nonlinear inversion

(e.g., Tarantola and Valette, 1982b). This method to solve of nonlinear equation like the

mutual impedance equation (Sunde, 1968) is justified when the initial solution is in the

neighborhood of the global minimum of the objective function. This is a reasonable

assumption where a good a priori knowledge of geology of field is available. Indeed, because

of numerous local minima in the objective function it is prevented the iterative optimization

techniques from working effectively.

Homotopy method is a powerful tool for solving nonlinear problems due to its widely

convergent properties (Watson, 1989). Homotopy was first used in geophysical applications

to solve the seismic ray-tracing problem (Keller and Perozzi, 1983). Vasco (1994 and 1998)

used homotopy to solve the inverse problem, illustrated its use for travel time tomography and

used to solve the regularized inverse problems in seismic problems. Everett (1996) applied the

method to solve the inverse electromagnetic problem based on a finite difference modeling.

Jegen et al. (2001) applied the classic Euler–Newton numerical continuation scheme to

inverse problem. Bao and Liu (2003) constructed a homotopy-regularization method to solve

inverse scattering problems with multi-experimental limited aperture data. Han et al. (2005)

used a homotopy method for the inversion of a two-dimensional acoustic wave equation.

The goal of this article is developing of the 1D inversion of IP and EM coupling

integral according to forward modeling code of Ingeman-Nielsen and Baumgartner (2006). A

homotopy method is applied to overcome the local convergence of Gauss-Newton and Quasi

Newton methods.

The plan of this paper is as follows. First, Background on EM coupling theory and forward

modeling and inversion process are reminded. Then, program structure is detailed. At last, the

results of inversion code for the synthetic data are presented.

2. Background on EM-coupling theory and forward modeling

In general, for two pairs of grounded electrodes at the earth’s surface, by definition, the

mutual impedance between the two electrode circuits is the ratio of the voltage in the

secondary to current in the primary.

)(/)()( 12 ωωω IEZ = (1)

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where I1 is the alternating current through the current electrodes and E2 is the electromotive

between the potential electrodes.

This mutual impedance involves a CR contribution due to the earth-return currents and an

induced coupling (IC) contribution due to induction between the wire loops above the ground

surface just as if the loops were not grounded (Brown, 1985). According to Sunde (1968), the

EM coupling between two grounded wires in an arbitrary configuration on the surface of the

earth can be calculated as an integration of mutual impedances of virtual dipoles along the

paths of the wires:

dsdSsS

rQrPZ

B

A

b

a∫ ∫

∂∂∂+= )(

cos)()(2

ξω

)()()()(cos)( BbQAbQBaQAaQdsdSrPB

A

b

a

+++= ∫ ∫ ξ (2)

where A, B and a, b are the end points of the transmitter and receiver wires (the grounding

points), dS and ds are infinitesimal elements of the two wires (the virtual dipoles), ξ is the

angle between the wire elements and r is the distance between them (Figure 1). Usually, when

dealing with EM coupling, the conductivity is considered constant and real and the

permittivity is most often neglected. With these assumptions on a homogeneous half-space,

the Q-function is real, constant (frequency independent), and only depending on the position

of the grounding points of the wires. It is therefore often referred to as the grounding function.

The P-function, although it contains a purely resistive term, is referred as the coupling

function.

One of the parts of forward modeling CR1Dmod (Ingeman-Nielsen and Baumgartner, 2006)

is dedicated to calculating EM response in the presence of CR effects. The software handles

frequency domain coupling for grounded wires. The wires may be divided into any number of

arbitrarily oriented linear segments, provided that the receiver and transmitter wires do not

intersect.

The usual practice is therefore to calculate a half-space response analytically based on the

properties of the first layer and add to this a correction term, which accounts for the summed

effect of the additional layering. Analytical solutions for the Hankel transforms in the P-

function of the grounded wire response are presented for non-magnetic homogeneous half-

spaces. Calculations can be performed using the full solutions, the new non-magnetic

approximation and the traditional quasistatic or low frequency approximation.

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3. Cole-Cole model

Many different models have been proposed for the description of the dispersive behavior of

the complex resistivity (Marshall and Madden, 1959; Van Voorhis et al., 1973; Vinegar and

Waxman, 1984), but the most widely used seem to be the empirical Cole-Cole model, which

was originally developed by Cole and Cole (1941) to describe dielectric dispersion. It was

shown by Pelton et al. (1978) to accurately describe the resistivity dispersion observed in field

data from areas with metallic mineral content. Recent works have shown that the Cole-Cole

parameters can be used to estimate the hydraulic conductivity of sediments (Binley et al.,

2005). The Cole-Cole model is given by:

( )

+−−= cj

mωτ

ρωρ1

111)( 0 (3)

where ρ0 is the resistivity in the DC limit, m is the chargeability, τ is the time constant and c is

the frequency dependence.

The Cole–Cole resistivity model is used in this forward modeling (Ingeman-Nielsen and

Baumgartner, 2006) that we used to inversion method.

4. Homotopy inversion theory

Homotopy is a method used to find solutions to general systems of nonlinear equations

L(P)=0.

A homotopy function H(P,λ) is constructed by adding to the “target function”L(P) a scalar

homotopy parameter λ and a second function g(P), so that

)()1()(),( PgPLPH λλλ −+= (4)

The “start equation” of nonlinear equations g(P)=0 can be chosen arbitrarily, the only

restriction is that it must possess at least one known solution, denoted by P=A.

For the initial value λ=0, the homotopy function H(P,λ) has a solution at A, since H(A,λ) =

g(A) = 0. With the aid of numerical continuation methods, starting from the known point A

and λ =0 a trajectory in (P,λ) space is mapped such that the homotopy function H(P,λ)

vanishes.

A solution P* of the target equation L(P)=0 occurs at any point where H(P,λ)=0, intersects

λ=1 since at these locations H(P*,1)=L(P*)=0. An application of homotopy methods to

geophysics is obvious if a geophysical inverse problem is formulated as a nonlinear equation

of L(P)=0, then all solutions P* satisfying L(P*)=0 that are found by the homotopy path-

tracking algorithm are solutions of the inverse problem (Jegen et al., 2001).

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5. Generalized nonlinear inverse problem

The knowledge of the probability law for each parameter, as shown by the Tarantola and

Valette (1982a):

( )( ))p(g

)p(g)p()p(

d

dpp µ

ρ⋅ρ=σ (5)

where:

(p)pσ is the a posteriori probability density for the vector of parameters p, (p)pρ the a priori

probability density for the data d, d = g(p), is the theoretical relationship may be considered

as exact, ( )g(p)dρ the probability density of the model and ( )g(p)dµ the null information (full

ignorance or homogeneous probability density HPD) on the parameter. This equation solves

the inverse problem for an exact non-linear theory with arbitrary a priori constraint on

parameters (pρ ) and an arbitrary probabilistic distribution of data ( dρ ).

For quasi-linear problems, if the relationship linking the observable data d to the model

parameters p, d = g(p), is approximately linear inside the domain of significant prior

probability, then the posterior distribution is just as simple as the prior distribution. For

instance, a gaussian a priori obviously leads to a gaussian a posteriori. In this case also, the

problem can be reduced to the computation of the mean and the covariance of the gaussian. It

is supposed hereafter, that the a priori information has a Gaussian form.

If the probability distributions are ‘bell-shaped’ (i.e., if they look like a Gaussian or like a

generalized Gaussian), then one may simplify the problem by calculating only the point

around which the probability is maximum, with an approximate estimation covariance matrix.

When one assumes that the probability densities are Gaussian:

( ) ( )

−−−=ρ −prior

1Tprior C

2

1const. ppppexp)p( pp (6)

( ) ( )

−−−=ρ −obs

1Tobs2

1const. ddCddexp)d( dd (7)

where Cp and Cd are covariance matrices parameters and data respectively. If we assume that

the nonlinearities are weak we obtain the followingleast square misfit function:

( ) ( ) ( ) ( )obs1T

obsprior1T

prior dpgCdpgppCppp dp −−+−−= −− )()()S( (8)

We apply the steepest decent algorithm (Gauss-Newton method) for the minimization of S(p)

function. If one considers the gradient αα ∂∂=γpS

, the Gauss-Newton algorithm is an iterative

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algorithm passing from point p to point 1k+p by the following function (Tarantola and

Valette, 2002):

( ) ( )( ) ( )[ ]priork1

obsk1T

k

11k

Tkkk1k C ppCdpgGCGCGpp

ppddppdd−+−×+−= −−−−−

+00000000

1ε (9)

where

priorp the initial estimation for the parameter vector p,

kp the estimated value at iteration step k,

00ppC the parameters covariance matrix (often diagonal by lack of knowledge);

00ddC the data covariance matrix (also diagonal for independent data),

kG and TkG are the derivative matrix of the data with respect to the parameters and its

transpose,

obsd the data vector,

kε is an ad-hoc (real, positive) value adjusted to force the algorithm to converge rapidly (if

kε is chosen too small the convergence may be too slow; it is chosen too large, the algorithm

may even diverge).

In the Gauss–Newton least-squares method, the Jacobian matrix is recalculated for all

iterations. The calculation of the Jacobian matrix can be the most time-consuming step of the

inversion process. In order to reduce the computing time, Loke and Dahlin (2002) used a

quasi-Newton method to estimate the Jacobian matrix values.

Jacobian matrix values can be calculated in first iteration. After each of iteration, the Jacobian

matrix is estimated by using the following updating equation:

Tkkk1k puGG ∆⋅+=+ (10)

Where kp∆ is the perturbation vector to the model parameters,

( ) kTkkkkk /. pppGgu ∆⋅∆∆−∆= , k1kk ggg −=∆ + , 1k+G is the approximate Jacobian matrix

for the (k+1)th iteration, kg is the model response for the kth iteration and kg∆ is the change

in the model.

In theory, the convergence rate of the quasi-Newton method is slower than the Gauss–Newton

method. While the quasi-Newton method might require more iteration to converge compared

to the Gauss–Newton method, the time taken per iteration can be much less. However, we

considered both methods in code.

Hereafter, the following hypotheses are considered:

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• Data, d, here a normally distributed Gaussian.

• Data are assumed to be independent from the parameters; it is simply stating that the

measurement action itself is without influence on the collected data.

• Parameters, p, for each horizontal layer is obtained by Cole-Cole model. Then invert

parameters are ρ0k, mk, ck, and τk respectively, static resistivity, chargeability,

frequency dependence, relaxation time and k is layer index.

• Homogeneous probability density (HPD) is taken constant; this term is not trivial and

Tarantola and Valette (1982a) propose to define HPD on a parameter from the

parameterization invariance with respect to a group transformation. In our case, the

parameters ρ0k and τk are positive and then its logarithmic character lead to state that

HPD for ρ0k is ( )[ ] .constlog k0 =ρµ and for τk is ( )[ ] constlog k =τµ . Here, ( )[ ]klog τµ

shows the null information or HPD for ( )kτlog . We considered

.constm1

mlog =

−µ and .const

c1

clog =

−µ (the change affecting m is

explained in details by Ghorbani et al., 2007).

• There is an explicit relationship d=g(p), where d is the data vector and p the parameter

vector to be sought; in our case, this is provided by equation 2. The relationship

d=g(p) is assumed to be exact.

6. Inversion process

In this section we explain the continuation (homotopy) inversion process considered here.

The input data consist of amplitude and phase at a number of frequencies that are converted to

real and imaginary resistivity values during the inversion processes. The measurements

should be performed for at least four frequencies spread over a suitably wide range since a

single simple Cole-Cole model has four parameters. The parameter vector p finally reduces to

[ ]Tiiii0i h,τ,c,m,ρ where )(ˆi0i0 ρ=ρ log , )

1log(ˆ

i

ii m

mm

−= , )

1log(ˆ

i

ii c

cc

−= , )log(ˆ

ii hh = and i is

layer index.

The first part is the determination of a 1D initial resistivity model from the DC apparent

resistivity values by an approximate inversion. The amplitudes of the apparent-impedance

values that are measured at the lowest frequency can be used as the DC resistivity values. To

invert the i0ρ and ih in initial model, mi is considered zero. Therefore in this case, forward

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modeling is similar to DC resistivity model. The Gauss-Newton method (equation 9) is then

used to construct the initial resistivity and thickness model.

The second part consist the homotopy method that use Gauss-Newton or Quasi-Newton

methods to minimization of misfit function in each step.

The parameters obtained in the earlier part are used to compute the starting model of the

homotopy inversion. We use a linear combination function of g(P):

)()1(),( 00 PgdPh λ−+λ=λ (11)

Where:

dobs the vector of in-phase and out-of-phase parts of complex resistivity measurements;

g0 the vector of real and imaginary resistivity obtained from forward modeling by starting

parameter vector p0 ;

p the parameter vector and

λ is a real variable that changes between 0 and 1.

Here, it is assumed that the physics-based forward response capable of predicting the data

vector, d=g(p*). The first value of λ is 0 and increases in later steps. It is clear that g(P,λ=0) =

g0(P0) is the same starting model vector. When λ increases, the other model vectors are

estimated so the effect of data measurements vector increases and the effect of the initial

model vector decreases. In this work, path tracking is based on a set of predictor-corrector

steps. The predictor step consists of varying the model vector (P,λ) by ∆λ along the λ-

direction (Benavides and Everett, 2006). We used an isometric division for ∆λ or N

jλ j =

where N,1,j L= as it proves to give satisfactory results (Benavides and Everett, 2006; Han

et al., 2007). The corrector step is a Gauss-Newton (or Quasi-Newton) algorithm that is used

for minimization of the misfit function in each step of homotopy inversion. Once the corrector

step is terminated, the next predictor step is initiated. At the j th predictor-corrector step, the

predicted model vector is (pk, j.∆λ). Assuming that the solution pj of the j th equation has

already been obtained, the successive Gauss-Newton (or Quasi-Newton) method can be used

to solve the (j+1)th equation. Then the iteration formula for solve j th step of homotopy

equation 11 with considering Gauss-Newton equation 9 is following:

( ) ( ) ( )( ) ( )[ ]priork1

jkk1T

k

1

kTkk

jk

j1k ppCphpgCGCGCGpp ppddppdd −+−×+−= −−−−−

+ 00000000,11 λε (12)

where k is iteration index of the Gauss-Newton iterations and T,k,,k L10= .

Or:

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( ) ( ) ( ) ( )

−+

+

−−×+−= −−−−−+ priork

1obsk

1Tk

11k

1Tkk

jk

j1k N

j

N

j1 ppCdpgpgCGCGCGpp ppddppdd 00000000 00ε (13)

The Jacobian-matrix values are obtained from numerical derivative of forward modelling.

Figure 2 shows the algorithm schema that is used during the inversion process.

7. Program structure

CR1Dinv consists of three main windows: CR1Dinv window, SondagePoint window and

Calculate window. CR1Dinv window controls the starting parameters and its standard

deviation and number of sounding data; SondagePoint window controls the configuration of

the sounding points; Calculate window controls the calculation specific parameters and

inversion routines. The left-hand side of CR1Dinv window features an interactive plot of the

half-space model (Figure 3). By mouse clicking into the plot, the user can insert layer

boundaries and drag them to the desired position. In the right-hand side of the same window,

the lower section gives input fields for the a priori layer parameters, including a priori Cole–

Cole model parameters and its standard deviation, relative permittivity (εr=ε/ε0) and magnetic

susceptibility (χ=µ/µ0-1), it also allows for adding and deleting layers in the model. The upper

right hand section of this window gives control of the measurement configurations. Dipole-

Dipole array and general surface array (GSA) are accessible. GSA allows for arbitrary

location of receiver and transmitter electrodes on the surface of the layered half-space.

Before entering the data, number of sounding points is determinate in this part. To enter the

new sounding data, one selects “new data” item from “File”. SondagePoint window (figure

4), has appeared and allows the user to enter the position of electrodes. At the bottom of this

window, there is a select field to enter the number of frequencies. We note that number of

frequencies is constant for all of sounding points. Therefore, before clicking to topview

button, it is necessary to select the number of measured frequencies. There is a column of

topview buttons on left hand of SondagePoint window. By left and then right clicking the

mouse on the topview buttons, a special window is called that allows the user to place the

electrodes, either by dragging them with the mouse, or by entering new coordinates in the

input fields, in left part of one. The topview windows also let the user add and move segments

of the receiver and transmitter wires. Thus, the influence caused by the placement of the wires

can be taken into account in the frequency domain responses. In the right hand of this window

is an Excel spread sheet that let the user enters the data spectrum (frequency in Hertz,

amplitude in ohm meter, negative phase in milliradian, Amplitude error in percent and phase

error in milliradian).

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In Calculate window (Figure 5), parameters specific to the type of calculation can be adjusted

before calling the forward modeling routine (Ingeman-Nielsen and Baumgartner, 2006) and

also specific inversion routines. For configurations allowing a choice (array configuration),

the frequency domain calculation is selected as well as the ‘‘full’’ or ‘‘quasi-static’’ modes. In

full mode, CR1Dinv selects either the full solution or the non-magnetic first layer solution

depending on the magnetic susceptibility specified for the first layer. In quasi-static mode, the

program assumes both non-magnetic and quasi-static approximations regardless of the

specified susceptibility (Ingeman-Nielsen and Baumgartner, 2006). Forward modeling and

inversion routines that calculate frequency domain response of the grounded wire

configurations and inverse problem are solved for that, emgsafwd.m and Inversion.m

respectively.

Different parameters that are used in the inversion part of Calculate window are following:

- The homotopy coefficient determines the maximum division number along λ-

direction. λ is the homotopy parameter that varies between 0 and 1.

- The improvement in the RMS error is considered as criterion for termination at each

homotopy inversion step.

- Gauss-Newton and Quasi-Newton options allow using for minimization of the misfit

function in each step of homotopy inversion.

- Iteration adjustment is the same ε ad-hoc (real, positive) value that is explained in

section 5.

After the calculations have ended, results are saved into a binary Matlab file along with the

model, configuration and inversed parameters.

Finally, calculated responses are plotted as Argand diagrams onto the screen. For each layer

plots present convergence processes for each of parameter.

8. Results

The results from two synthetic examples with the inversion method are presented. Minimum

version is a Matlab environment version 7.0.4 (R14). We used 17 frequencies in the 0.183 Hz

to 12 kHz range with a logarithmic step NkHz 2/12 where N is number of frequency used in

the SIP FUCHS-II equipment (Radic Research).

The first example model consists of a half-space earth. Table 1 shows the real and inversion

values of parameters. The amplitude and phase values are calculated for 5 sounding points,

obtained from a Dipole-Dipole array. The distance array line AB=MN=50 m and n, Dipole-

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Dipole separation, changes from 1 to 5. Transmitter and receiver cables are in same line. The

recovered parameters agree well with the true values. The number of parts in λ-direction is 10

(∆λ=0.1). Root mean square error (RMS) is obtained 0.3%.

We used inversion process for different starting parameter vectors and traced path tracking

curves (the curve that is obtained by parameters versus λ where 0),( =λPh in equation 11).

The results show that all the path tracking curves converges true value (Figure 6).

The second test model consists in a two horizontal layers mode with thickness of upper layer

5 m. Table 2 shows the model and inverted parameters. The amplitude and phase values are

calculated for 5 sounding points, obtained from Schlumberger array. The transmitter lines AB

change from 0.6 to 60 meter. Transmitter and receiver cables are in same line. The other

conditions that are supposed to inversion process are:

- The homotopy inversion consist 5 steps.

- The Quasi-Newton is considered for misfit minimization.

Table 2 shows the recovered electrical parameters agree well with the true values.

9. Conclusion

A homotopy inversion method for SIP data using the Cole-Cole model is proposed

based on electromagnetic formulation of a 1D earth. This method further widens the domain

of convergence of traditional methods. In this work, path tracing is based on a set of

predictor-corrector steps. The predictor step consists of varying the model vector (P,λ) by ∆λ

along the λ-direction. Locally inversion methods of Gauss-Newton and/or quasi Newton are

used as corrector step. Homotopy parameter λ is divided isometric.

An approximate inversion of the DC resistivity model is first carried out to construct the

initial resistivity and thickness models, and this is then used as the starting model in the final

inversion.

The inversion results show the recovered parameters agree well with the true values.

We test the inversion results with field data in a future paper.

Acknowledgement

We are indebted to the INSU-ECCO program (project Polaris II, 2005-2007) in France for

support to this work.

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25, 29-51.

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Captions

Figure 1: Earth model and grounded wire in common array of two wires on the

surface. A, B and a, b are the end points of the transmitter and receiver wires, respectively. dS

and ds are infinitesimal elements of the two wires, ξ is the angle between the wire elements

and r is the distance between them. ρ*(z) indicates the complex resitivity in Z direction.

Figure 2: Simple schema of inversion algorithm.

Figure 3: CR1Dinv window: a graphical representation of the model, in which the user

can add or delete layers and move boundaries. Right-hand side of the window gives control of

the configuration, a priori layer parameters and a priori layer parameters standard deviation of

the model.

Figure 4: Sounding point window of CR1Dinv features a spread sheet that allows

entering the electrodes coordinate. Left and then right Click the mouse gives access to topwive

windows as edit the cable configuration of each sounding point.

Figure 5: Calculate window of CR1Dinv gives user control over calculation domain,

transform types, tolerances and spline interpolations.

Figure 6: Homotopy path tracking curves of Cole-Cole chargeability parameter on a

complex reistivity half space earth. Homotopy parameter lag ∆λ=0.1 is constant. The

chargeability values vary in starting parameters models.

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Tables

Table 1: Inversed parameters are obtained during inversion algorithm for synthetic spectral induced polarization data. Earth is proposed half-space. Real values of parameters are presented.

Layers Parameters

ρ0(Ωm) m c τ(s)Standard deviation of

parameters

0ρ m c τRMS error

(%)

Real values 50 0.8 0.3 10-1

Inversion values 1

49.98 0.7998 0.300 0.0998 1 0.5 0.5 1 0.3

Table 2: Inversed parameters are obtained during inversion algorithm for synthetic spectral induced polarization data. Earth is proposed containing two layers. Real values of parameters are presented.

Layers

Parameters ρ0(Ωm) m c τ(s) h(m)

Standard deviation of parameters

0ρ m c τ h

RMS error (%)

Real values 50 0.30 0.30 1 5

Inversion values 1

49.9 0.30 0.30 0.97 4.96 1 0.5 0.5 1 0.1

Real values 300 0.05 0.80 0.01 -

Inversion values 2

299.7 0.05 0.77 0.01 - 1 0.5 0.5 1 -

2.6

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Figures

Figure 1

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Figure 2

Hom

otopy algorithm

A priori Entering: N: number of layers

Parameters: ρ0i,mi,ci,τi and hi

Standard deviation of parameters

[ ]TP iiii0i h,τ,c,m,ρ0 =)( 00 Pg

10 ≤λ<

)()1(),( 00 PgdPg λ−+λ=λ

Gauss-Newton or Quasi-Newton algorithms

Initial parameters vector: P Data vector: g(P,λ)

New P

λ=1

Yes

No Increase λ

Determinated P*

DC-resistivity inversion (Gauss-Newton method)

i0ρ andih

Search for starting point

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Figure 3

Figure 4

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Figure 5

0 0.2 0.4 0.6 0.8 1λ

0

0.2

0.4

0.6

0.8

1

m

Real parameters m*=0.8, ρ∗0=50 Ωm, c*=0.3, τ∗=0.1 s

initial parameters:m=0.01, ρ0=100 Ωm, c=0.1, τ=10 s

m=0.99, ρ0=100 Ωm, c=0.1, τ=10 s

m=0.49, ρ0=100 Ωm, c=0.1, τ=10 s

Figure 6

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Non-invasive monitoring of water infiltration in a silty clay loam soil using

Spectral Induced Polarization

A. Ghorbani*, Ph. Cosenza*, S. Ruy#, C. Doussan

#, N. Florsch*

* UMR 7619 Sisyphe, Université Pierre et Marie Curie-Paris6, CNRS, Paris, France # INRA- UMR Climat, Sol Environnement, Avignon, France.

Abstract: An experimental investigation was undertaken to study the ability of Spectral

Induced Polarization (SIP) to monitor water infiltration in a silty clay loam soil. It was based

on the coupled acquisition of tensiometer data and Spectral Induced Polarization (SIP) spectra

(1.46 Hz to 12 kHz) during the infiltration event created by an artificial constant rainfall rate

of about 15 mm/hr.

The approach, which was applied both in the field and in a soil column, confirms the

existence of a significant phase drop in the high-frequency domain (typically greater than 1

kHz) during the first infiltration cycles. The interpretation of the tensiometer and SIP data

show that this phase drop is correlated with the water filling of pores in the [30-85] m

diameter range.

The phase drop is qualitatively and quantitatively interpreted as a Maxwell-Wagner effect

associated with the electrical heterogeneity of the soil. It could correspond to the transition

between two physical states. In the first state before the arrival of the wetting front, highly

polarized and wet aggregates are embedded in an electrically isolating phase, i.e. air. In the

second state after the arrival of the wetting front, structural pores between the aggregates are

filled with a connected and conducting phase i.e. water, leading macroscopically to a decrease

in bulk soil polarizability.

The experimental and theoretical results of this study suggest strongly that the SIP method

can be used to monitor the water filling of structural or draining pores in the field. This

original result requires validation in other sites.

Keywords: Spectral Induced Polarization, complex resistivity, infiltration.

Index terms: 0925 Exploration Geophysics: Magnetic and electrical methods (5109).1835 Hydrology:

Hydrogeophysics. 1838 Hydrology: Infiltration. 1875 Hydrology: Vadose zone

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1. Introduction

Both dielectric and electrical methods have been used for decades in soil science in order

to quantify the changes in soil water content and soil salinity [e.g., Smith-Rose, 1933].

Dielectric methods, which measure the relative dielectric permittivity in the few dozen MHz

to 1 GHz frequency range, include (a) time domain reflectometry (TDR) probes [e.g., Davies

et al., 1977], capacitance sensors [e.g., Tran Ngoc et al., 1972] and ground-penetrating radar

[e.g., Chanzy et al., 1996]. The electrical methods, which are often called DC (Direct Current)

or low-frequency electrical techniques and measure the electrical conductivity (EC) in the few

Hz to 10 kHz frequency range, include (a) low-cost electric resistance methods (gypsum

block for matric potential measurements) [e.g., Bouyoucos and Mick, 1940] and (b) four-

electrode methods used both in the laboratory and the field [e.g., Tabbagh et al., 2000].

In electrical methods, the measured EC is an in-phase conductivity and is associated with

the in-phase conduction of the reference electric current. However, the measured electrical

impedance is generally a complex quantity with a corresponding in-phase and quadrature

component [e.g., Keller and Frischknecht, 1982; Ward, 1990]. In the frequency domain, this

quadrature conduction is related to a phase shift between the measured voltage and the

applied alternative current. The quadrature conduction at low frequencies (typically from 10

mHz up to 10 kHz) is referred to in geophysics as induced polarization (IP), complex

electrical conductivity or complex resistivity. The method used to measure the spectra of

these complex quantities is called Spectral Induced Polarization (SIP).

Initially, the IP method was developed for detecting small concentrations of disseminated

mineralization in base metal exploration [e.g., Marshall and Madden, 1959; Van Voorhis et

al., 1973]. However, recently, attention has focused on IP in rocks and soils as a means of

determining surface properties indirectly (cation exchange capacity and specific surface area)

[Vinegar and Waxman, 1984; Olhoeft, 1985; Boerner and Schön, 1991; Slater and Glaser,

2003; Lesmes and Morgan, 2001; Slater et al., 2005] and hydraulic conductivity [Boerner et

al., 1996; Lima and Niwas, 2000; Comas and Slater, 2004; Binley et al., 2005; Tong et al.,

2006]. The experimental investigations of Titov et al. (2002) and Scott and Barker (2003)

showed that pore-throat diameters and pore geometry in water-saturated geomaterials

contribute significantly to both in-phase and out-phase conduction at low frequencies. IP

measurements performed on unsaturated sands submitted to various infiltration-drainage

cycles have shown that IP parameters exhibit a complex saturation dependence and are a

function of saturation range and saturation history [Ulrich and Slater, 2004]. Titov et al.

[2004] confirmed the previous results and proposed an IP model for unsaturated sands. This

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model is able to detect the critical water saturation, which corresponds to the change in pore-

water geometry from bulk water to an adsorbed film existing on the quartz grains. However,

not all of the aforementioned experimental investigations examined natural soils with an

associated broad distribution of particles, pores and aggregate sizes.

In summary, although the IP method has become increasingly popular in environmental

and groundwater investigations [e.g., Binley and Kemna, 2005; Boerner, 2006], its full

potential has yet to be realized in hydrological sciences, especially in topics related to flow

and transport in partially saturated soils.

Indeed, among these topics, the non-invasive characterization of water infiltration in

unsaturated soils is still an active field of research [e.g., Dingman, 2002]. Although the DC

electrical method has been reported to be able to monitor flows in the vadose zone [e.g.,

Hagrey and Michaelsen, 1999; Zou et al., 2001], the IP method has never been used for this

purpose. The aim of this work was to address experimentally the capabilities of the SIP

method for characterizing vertical flows in the vadose zone during an infiltration test.

Our approach is based on both field and laboratory experiments that couple SIP

measurements and hydraulic measurements as performed in a natural agricultural soil.

First, the IP (and hence SIP) method and the underlying physical mechanisms are briefly

reviewed and the various IP parameters are discussed. The field and laboratory experiments

are presented in the second and the third part of the paper, respectively. Finally, the results are

discussed in the fourth part.

2. Induced Polarization: theoretical and phenomenological aspects

2.1 Complex electrical properties

The concepts of complex conductivity and complex resistivity are directly related to

Maxwell’s postulate: the total electric current density Jt is the sum of the conduction current

density Jc and the displacement current density Jd, which are both defined by the following

constitutive equations for time harmonic fields [e.g., Guéguen and Palciauskas 1994]:

EEJ c1

(1)

ED

J d 0it

(2)

where is electrical conductivity, is electrical resistivity, E is applied electric field, D is

the electric displacement, t is time, i is 1 , 0 is the permittivity of the vacuum and is

the complex relative permittivity. Equation (1) is referred to as Ohm’s law.

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Consequently, by using equations (1) and (2), the total current density can be expressed as

EEEJJJ dct*

1*)i( 0 (3)

where * and * are the complex conductivity and the complex resistivity, respectively.

By comparison with (2), equation (3) can be rewritten in order to introduce an effective

complex relative permittivity eff*:

EJ efft 0i * (4)

The complex electrical properties, *, * and eff* are linked with each other by the

following relationships:

**

* eff0i1

(5)

Generally, these complex properties measured in earth materials are frequency dependent,

i.e. they show an electrical dispersion. They can be split into two parts, i.e. a real component

and an imaginary (or in-phase and quadrature) component. They can also be expressed in

polar form as a magnitude and a phase. For instance, complex resistivity can be written as:

)exp(*'''* ii (6)

where ’, ’’ and * are the real part, the imaginary and the resistivity amplitude of

respectively, and is the phase of that can be also written as follows:

)mradsiftypically('

''

'

''tan 1001 (7)

or from equation (5):

)mradsiftypically('

''

'

''tan

''

'tan

eff

eff10011 (8)

where ’eff and ’’eff are the real and imaginary parts of the complex relative permittivity

respectively. Parameters ’ and ’’ are the real and imaginary parts of the complex

conductivity respectively.

2.2 Polarization mechanisms and models in the low frequency range

The purpose of this section is not to establish an exhaustive summary of the experimental

and theoretical works devoted to polarization mechanisms but to give the main physical

concepts widely used. For a comprehensive review of such works, the reader is referred to

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Chelidze and Gueguen [1999], Lesmes and Morgan [2001], Santamarina [2001] and

references therein.

In general, any mechanism, which restrains the relative displacement of charges, can be

considered as a polarization mechanism (charge displacement without restriction renders

conductivity) [e.g., Santamarina, 2001]. This leads to an accumulation of negative charges,

(i.e. an electrical pole) on one side of the medium and positive charges (i.e. another pole) on

the opposite charges. In effect, the medium becomes polarized.

In the low frequency ranges (typically from 10 mHz up to 10 kHz), the restrained relative

displacement of charges in geomaterials may have two origins.

The first origin is electrochemical and it is related to the existence of an Electrical Double

Layer (EDL) at the interface between solid and liquid phases. The EDL results from usually

negative electrical surface charges existing in the solid particles and appears at the solid-liquid

interface, as an oppositely charged ion atmosphere. In the EDL, the average concentration of

cations (in the case of negatively charged surfaces) is larger than that of anions. There are two

clearly distinguishable groups of electrochemical mechanisms and models. In the first group,

models have been introduced to account for the dielectric response of dilute suspensions of

spherical particles from Colloid Science [e.g, Lyklema, 1995] (Figure 1a). In the second, the

Marshall-Madden model has been especially proposed for rocks with a dispersed clay fraction

[e.g., Marshall and Madden, 1959]. In this model, rock is considered as a serial connection of

active (ion-selective) and passive (non-selective) zones. Clay minerals coating the quartz

grains or located in pore throats [Ward, 1990] and pore throats themselves associated with an

EDL [Scott and Barker, 2003; Titov et al., 2002] are selective zones (Figure 1b and 1c). The

first case in which clay minerals play a significant role is often called “membrane

polarization” (Figure 1b). These active and passive zones have different transport Hittorf

numbers, which produces local concentration gradients under applied external voltage. These

concentration gradients induce local solute flows and hence an additional electrical current

leading to the phase shift and the frequency dependency of the resistivity observed in IP

measurements [Titov et al., 2002].

The second main origin of low-frequency polarization in earth materials is geometrical

and interfacial (GI). The GI or spatial polarization mechanism results from differences in

conductivity and polarizability among components in a mixture, producing charge

accumulation at the interface. The first calculation related to GI polarization was made by

Maxwell [1891], who considered layered materials (Figure 1d and Figure 1e). As Wagner

[1924] solved the complex permittivity of a dilute suspension of conductive spheres (Figure

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1f), interfacial polarization is also known as the Maxwell-Wagner effect. This mechanism,

which can be seen as a bulk effect, has a pure macroscopic definition and does not require any

comprehensive understanding of the physical process of charge accumulation at the molecular

level.

The most popular formulation for modeling the Maxwell-Wagner effect in Earth Sciences

is the Maxwell-Wagner-Hanai-Bruggeman (MWHB) equation [e.g., Chelidze and Guéguen,

1999; Lesme and Morgan, 2001; Cosenza et al., 2003], which corresponds to a Differential

Effective Medium (DEM) theory. Consider a mixture of two components: spheroidal

inclusions with an effective complex permittivity i are embedded in a matrix characterized

by an effective complex permittivity m. The effective complex permittivity of the mixture

mix is given by the MWHB equation:

i

m/

mix

m

mi

mixi d1

1

(9)

where di is the volume fraction of spheroidal inclusions, m is a particle shape factor

related to the eccentricity of the spheroidal inclusions and is also called the “cementation

exponent”. Obviously, from equations (5), the MWHB equation (9) can also be expressed in

terms of complex conductivity or complex resistivity. Thus, Samstag and Morgan [1990]

used a similar equation expressed in terms of complex conductivity to model the IP of

saturated shaly sands.

The GI and electrochemical models are not incompatible since they operate at different

scales. For instance, Lesmes and Morgan [2001] proposed a granular model for the electrical

properties of saturated sedimentary rocks that combines both approaches. On the basis of their

model, the MWHB equation was considered as a mixture formula in which the

electromagnetic properties of components, especially the clay fraction, are governed by

microscopic and physico-chemical laws.

3. Field experiments

3.1 Soil, experimental set-up and procedure

Field experiments were undertaken on a silty clay loam soil of an agricultural INRA field

site located near Avignon in Southern France. The A horizon (0-60cm) is made of a tilled

layer (0-30 cm) overlapping an undisturbed layer with centimetric (0-15 cm layer) to

decimetric (15-30 cm layer) polyhedric clods. The main characteristics are given in Table 1.

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A square plot of 0.99 x 0.99 m was established (Figure 2). A trench about 30 cm deep was

dug around the perimeter of the plot. A PVC wall was placed in the trench against the inside

wall of the plot, except on one side so that possible runoff water could drain away (Figure 2).

Twenty-four automatic pressure transducers connected to micro-tensiometers (2.2 mm in

diameter, SDEC France) were placed in the plot 20 cm and 40 cm apart at depths of 8 cm and

13 cm (Figure 2). The 24 tensiometers were grouped into 4 subgroups by 4 switching boxes

connected to a datalogger (CR10X, Campbell Sci).

SIP measurements were carried out with the SIP-FUCHS II device (Radic Research)

which measures complex resistivity over 7 decades of frequency (1.4 mHz up to 12 kHz) with

4 electrodes. It consists of two remote units that record current I injected by two electrodes A

and B and voltage U signals measured between two electrodes M and N (Figure 2). The

apparent complex resistivity * is given by:

)(ie)(*I

Ua)(* 2 (10)

where (i2=-1); a is the electrode separation; )(* and )( are the resistivity

amplitude and the phase respectively. They are a priori a function of the angular frequency .

Equation (10) gives an “apparent” value of the resistivity, which is the resistivity of a

homogeneous ground that will give the same impedance for the same electrode array.

To measure the whole spectrum of both parameters, )(* and )( , the SIP FUCHS-

II apparatus starts with the highest frequency, 12 kHz, and the N other decreasing frequencies

are obtained by the following division: 12 kHz/2N. Optical fibers are used in order to

minimize electromagnetic cross-couplings between the transmitter and the receiver and to

ensure a system-wide synchronization. The measured data are transferred to the base unit,

where the impedance amplitude and the phase shift are determined. The SIP FUCHS-II is

connected to a computer in order to record the data and to display the results in real time.

To minimize the so-called “electrode polarization” associated with electrochemical

reactions occurring at the electrode-sample boundary [e.g., Chelidze et al., 1999], the A and B

current electrodes were Cu/CuSO4 electrodes whereas the M and N electrodes were Pb/PbCl2

electrodes [e.g., Petiau, 2000].

With this experimental set-up and within the impedance range of 1-10 kOhm, the absolute

impedance error is less than 0.1 %. Within the same impedance range and for frequencies less

than 1 kHz, the phase error was estimated to be less than 1 mrad. When the frequency is in the

range of 1 kHz to 12 kHz, the phase error increases to 1 mrad.

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The electrodes were vertically installed in the plot. A Wenner array was used with the

electrodes 20 cm apart. In this array, the four electrodes are collinear and the intervals

between adjacent electrodes are equal (Figure 2). If a homogeneous soil is being studied, the

depth of investigation of such an array, for which the sensitivity to vertical changes in

electrical properties is maximum, is about 10.4 cm, i.e. ABx0.519 [e.g., Edwards, 1977],

which is between the two depths of the tensiometers. Nevertheless, it should be borne in mind

that: (a) the value of 10.4 cm is an order of magnitude used for planning the field experiment

since the studied system (water front displacement in a dry soil) is intrinsically

heterogeneous; (b) the measured amplitude and phase are complex averages of these

parameters over the depth of investigation, so they are not local measurements, as is the case

for tensiometer measurements.

Water infiltration in the soil was achieved by a rainfall simulator (Institut de Recherche

pour le Développement-IRD model) which provided a constant rainfall rate in the range of

10-100 mm.hr-1

. Fresh water taken from the water table located at the site was used as the

wetting fluid for all experiments. Its conductivity was equal to 930 S/cm at 20 °C.

The field experiment was conducted in two main phases (Figure 3). First, an infiltration

test (Test 1) with a rainfall rate of 15.4 mm/h was performed for about two hours. Before,

during and after this rainfall event, an electrical resistivity spectrum between 1.46 Hz to 12

kHz was measured every two minutes. As the soil was initially in a dry state (initial

volumetric water content of 0.240 m3.m

-3, which corresponds to a matric potential lower than

– 10 m), tensiometers were inserted into the soil only 30 min before the beginning of the

rainfall simulation in order to avoid their desaturation. It follows that the first pressure

measurements are not representative of the soil water matric potential as the tensiometers

were not in equilibrium with the soil water. Representative measurements are obtained only

after the arrival of the wetting front at the depth of insertion. In the second phase (Test 2 in

Figure 3) one day later, a new infiltration test with a higher rainfall rate of 32.4 mm/h was

carried out for about one hour. The soil was wet (matric potential about -0.35 m which

corresponds to a water content of 0.350 m3.m

-3). Electrical resistivity spectra were measured

again with the same procedure as in Test 1, except for the frequency range: 0.732 Hz to 12

kHz. During both phases, the soil water matric potentials were recorded with a 10-s sampling

interval.

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3.2 Results

During Test 1, no surface ponding occurred at any time. The rainfall rate was equal to the

infiltration rate into the soil. The matric potential measurements located at the same depth, as

indicated in Figure 4 for six tensiometers, showed significant differences in terms of

amplitude and temporal dynamics. This spatial variability is also illustrated in Figure 5 where

the times corresponding to the arrival of a wetting front (i.e. fast increase of the matric

potential, becoming less negative) are plotted. Both figures confirm an infiltration process

associated with a significant spatial heterogeneity of the structured soil studied.

To compare these results with geophysical measurements in order to obtain average

values of SIP parameters over about 10 cm, tensiometer values were averaged for the two

groups of 12 tensiometers located at the two depths, 8 cm and 13 cm (Figure 6). The average

value at 13 cm clearly shows that, during water infiltration, the initial and rapid increase of

the matric potential (at 22 min) was stopped at about 50 min, after which the matric potential

evolved more slowly. The time of 22 min (respectively 50 min hereafter referred to as td) is

interpreted as the average time for the wetting front to reach the depth of 13 cm (resp. as the

average time to reach the steady state).

During Test 1, both components (phase and resistivity amplitude) of the complex

resistivity spectrum vs. time are given in Figures 7 and 8. The resistivity amplitude decreased

during water infiltration and increased slowly when rainfall was stopped (Figure 7). The good

sensitivity of resistivity amplitude to soil water content changes is already known: resistivity

is a decreasing function of soil water content [e.g., Rhoades et al., 1976]. Moreover,

resistivity amplitude measurements show a very weak frequency dependence: the observed

resistivity spectra were flat. This classical feature justifies the use of low-frequency electrical

techniques for measuring soil Direct Current (DC) resistivity [e.g., Tabbagh et al., 2000].

In comparison with amplitude, phase displayed a more complex behavior (Figure 8). Early

during water infiltration, the phase angle increased slowly but significantly as the water

content increased in the first centimeters of the soil. However, at time td (see arrow in Figure

8), the phase measured in the high frequency domain had dropped significantly with a higher

level of noise. This rapid drop, which was not observed in the lower part of the frequency

range, is related to the arrival of the wetting front in a zone where the sensitivity of the

electrical parameters is maximal. Since this drop mainly concerns the phase measurements at

time td and is enhanced in the higher part of the frequency range, a GI polarization mechanism

was suspected to occur during the wetting front diffusion. This assumption will be discussed

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on the basis of results provided by a laboratory investigation and a subsequent model, both of

which are presented in the last section.

During infiltration, the phase continued to decrease slowly with a significant level of

noise, likely related to the heterogeneity of the soil and the associated water movement. When

the rainfall stopped, the phase returned almost to the initial level existing before the phase

drop, and thereafter decreased slowly during the drainage phase. It should be noted that this

phase reversibility was not associated with a hydraulic reversible behavior, as indicated in

Figure 6.

Concerning Test 2, the matric potential prior to infiltration (Figure 9) was higher

compared to Test 1 before the application of the rainfall rate. One-day drainage, redistribution

and evaporation did not restore the initial soil-water state that existed before Test 1. A small

amount of ponding was observed during Test 2. The resistivity spectra shown in Figure 10

were still sensitive to water content changes induced by water infiltration. The phase values

were lower than those obtained during Test 1 (Figure 11). Moreover, contrary to Test 1, the

phase spectra did not show any significant correlations with the transient matric potential

variation given in Figure 9. Indeed, the phase drop observed during Test 1 was not detected

during Test 2. This physical phenomenon is consequently related to a dry soil and possibly to

a characteristic size of air-filled pores, above which the phase drop would not exist. This

aspect will be discussed hereafter.

In summary, the results of this field experiment confirm the practical interest in using

resistivity measurements to monitor soil water content but also demonstrate a surprising phase

drop occurring during water infiltration in a dry soil. This peculiar pattern associated with

phase measurements has not observed in the literature to date and requires further

experimental and theoretical work.

4. Column experiments

4.1 Objective, experimental set-up and procedure

The objectives of this laboratory study were: (a) experimental confirmation of the phase

drop measured in the field; (b) characterization in controlled conditions in order to

substantiate a physical mechanism.

The laboratory PVC column (Figure 12) was 280 mm high, had a 150 mm internal

diameter and was filled with undisturbed core soil from the field experiment. Soil sampling

was carried out carefully in order to obtain an undisturbed and representative soil sample in a

dry state. The first 15 cm layer of the column was cloddy whereas the bottom part of the soil

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core was more massive. The column contained 10 micro-tensiometer ports located at depths

given in Figure 12.

The infiltration events were simulated by a rainfall simulator which was calibrated to

provide a rainfall rate similar to that applied during the field experiments (i.e. 15 mm/hr). The

simulator area was close to that of the column in order to constrain the wetting profile to one

dimension. The base of the column was not sealed in order to maintain a drained condition.

The drainage water was weighed and its electrical conductivity was measured. The electrical

conductivity of the infiltration water used for the experiment was 660 µS cm-1

.

A laboratory complex resistivity system (1253 Gain-Phase analyzer Solartron

Schlumberger) was used for electrical data acquisition. Four Cu/CuSO4 electrodes were

positioned in a horizontal plane located at 7 cm depth (Figure 12) where the soil structure was

the most similar to that in the field. This electrode configuration offers two advantages. First,

it makes it possible to test a very different configuration compared to that used in the field, i.e.

the sensitivity of the geometric electrode array compared to the main direction of the water

infiltration can be estimated. Second, its maximum sensitivity is in the electrode plane, i.e. the

influence of the physical processes located at the top and the bottom of the column is

minimized. Three high frequencies were considered: 93.5 Hz, 187 Hz and 1.5 kHz in order to

speed up the acquisition process with a high rate of sampling. Note that all three frequencies

were also used by the SIP FUCHS-II field device. Moreover, in this laboratory configuration,

the apparent complex resistivity is not given by equation (10): a new geometric factor, i.e. the

2 a term in equation (10), had to be calculated. This factor related to the electrode

configuration was quantified numerically by solving the Laplace equation with a finite-

difference scheme.

With this experimental set-up and within the impedance range of 1-10 kOhm, the absolute

impedance error and the phase error were estimated to be less than 0.1 % and 2 mrad,

respectively.

The laboratory experiment was conducted in two cycles (Figure 13). Each cycle consisted

in an infiltration step by application of rainfall and a subsequent free drainage step with no

applied rainfall. During both infiltration and drainage cycles, the matric potentials and the SIP

parameters were recorded with a 2-minute sampling interval.

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4.2 Results

Figures 14 and 15 show the matric potential variation during the first infiltration-drainage

cycle. The results confirm that the water flow is vertical, one-dimensional and homogeneous

at least until a depth of about 10 cm (Figure 14). On the other hand, the matric potential

readings in the lower part of the column (Figure 15) strongly suggest that the infiltration

became complex and preferential: the tensiometer C5 located at a depth of 20 cm reacted

before the tensiometer D5 located at a depth of 17 cm. Moreover, the response time lag

between tensiometers D1 and C6 located at the same depth (23 cm) was greater than 10

minutes (Figure 15).

Figure 16 shows the evolution of the resistivity amplitude during the first infiltration-

drainage cycle for the three frequencies, 93.7 Hz, 187 Hz and 1.5 kHz. The results again

validate the good sensitivity of resistivity to soil water content changes, i.e. the resistivity

evolution reacted immediately when the rainfall rate was applied or stopped. They were also

weakly frequency-dependent, as were the field measurements. Nevertheless, the results show

two features that were not observed in the field: (a) a resistivity peak was recorded at time 20

min; (b) the resistivity began to increase at time 66 min during water infiltration, whereas the

soil water content continued to increase.

The first feature, i.e. the resistivity peak, is clearly associated with the arrival of the water

front at the maximum sensitivity plane of the electrode array (see the C2 tensiometer

evolution located at the same depth of 7cm). It can be interpreted as a classical “à-coup-de-

prise” which is usually observed in electrical investigations when a current electrode (A or B)

is placed in contact with a highly resistive or conductive heterogeneity. This phenomenon is

enhanced when high and shallow contrasts of resistivity exist at the soil surface. Moreover, it

is interesting to note that a similar peak was observed in a rather different context during the

migration of a hydrocarbon liquid through a porous medium within a laboratory column

[Chambers et al., 2004].

The second feature (the increase of resistivity) is clearly related to the first arrival of water

at the base of the column (Figure 16). Since resistivity is primarily a function of salinity and

water content, the resistivity increase is here interpreted as a decrease in the salinity of the soil

solution. As the infiltration process evolves, the percolating fresh water interacts

geochemically with the solid and the initial water of the micropores, which is usually more

concentrated [e.g., Blackmore, 1978]. As the seepage began at the base of the column and as

fresh water was provided continually into the column, the pore water became more and more

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diluted by the fresh water. The EC of the retrieved water during the first 2 hours of drainage

was greater (1713 µS/cm) than the irrigation water (660 µS/cm).

The phase evolution during the first infiltration-drainage cycle is shown for the three

frequencies in Figure 17. The values of the tensiometer C2 located at the same depth (i.e.,

7cm) are also given in the same figure. In comparison with the field measurements, the

laboratory results confirmed the rapid phase drop during the water infiltration. This phase

drop, which is clearly associated with the water front past the plane of electrodes, is also

frequency-dependent and is higher for the highest frequency (~ 15 mrad at 1.5 kHz). As for

the resistivity measurements, an inverse phase peak was also detected, which might have the

same cause, i.e. an “à-coup-de-prise”.

However, contrary to the field experiment, an additional feature was present, i.e. the

transient phase evolution was less noisy and erratic than that measured in the field. In our

opinion, this feature seems to confirm the relationship between the electrical noise recorded

for the phase measurements and the level of heterogeneity of the studied system. The good

signal-to-noise ratio obtained in the laboratory is likely due to the location of the zone of the

electrical maximum sensitivity in a homogenous part of the soil column, whereas the poor

signal-to-noise ratio obtained in the field was mainly the consequence of preferential flow

water in a heterogeneous soil at the scale of the electrical set-up (see Figures 5a and 5b).

Moreover, contrary to the field experiment, the phase did not increase when the rainfall

stopped. This point can be explained by the relatively good homogeneity of the soil column in

the plane of the measurement electrodes. Contrary to the field experiment where macropores

with different sizes played a significant role, the soil involved in the column experiment was

likely associated with much smaller draining pores, which were still saturated when the

rainfall stopped. On the other hand, in the field experiment, the numerous larger pores drained

off rapidly as the rainfall ended. Consequently, as discussed hereafter, this comparison

suggests that draining pore size is a key parameter in understanding the evolution of the

measured polarizability.

The resistivity amplitude and the phase measured during the second infiltration-drainage

experiment are plotted in Figures 18 and Figure 19, respectively. As was the case during the

first cycle, the evolution in resistivity amplitude exhibited the same transient signature with

the same salinity effect during the water seepage at the base of the column. However, no

resistivity peak was observed. This can be explained by a much lower contrast between the

conductivity of the percolating water and that of the background.

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Similarly to the field experiment during Test 2, no significant phase drop was measured

during the second infiltration-drainage cycle: the phase measurements were almost

independent of the infiltration history of this cycle.

In summary, the laboratory measurements confirmed that the field observations: the SIP

parameters, i.e. the resistivity amplitude and the phase, are saturation-dependent [e.g., Ulrich

and Slater, 2003]. Moreover, the results validate the phase drop evidenced during water

infiltration in the field in a dry soil. The existence of this phase drop does not depend on the

electrode arrangement relative to the major direction of the water flow. At this stage, in order

to use the SIP approach for characterizing vertical flows in soils, it is necessary to provide

some physical hypotheses to explain this new and original result. This is the main objective of

the following section.

5. Discussion

Our purpose in this section is not to provide a quantitative model of the field and

laboratory experiments. There are at least two reasons for this. Firstly, from a hydrological

point of view, the results show that the vertical flows were complex and likely preferential in

both cases. Moreover, many of the hydraulic parameters (hydraulic conductivity, distribution

of the initial porosity and water content etc.) are unknown. Secondly, from a geophysical

point of view, complex apparent resistivities were measured that are not intrinsic soil

parameters: these apparent parameters depend on the electrode arrangement so a

multielectrode system with a specific inversion model would be necessary in order to obtain a

spatial distribution of the intrinsic parameters.

The ensuing discussion focuses on the phase drop measured in both experimental studies,

which showed the following features:

The phase drop exists whatever the electrode arrangement (at least for the two

configurations used in this study). It seems to be enhanced when the plane of the

electrodes is perpendicular to the main direction of the water front.

It occurs only if the soil is initially in a dry state, typically here with a matric

potential lower than a few meters (Figures 6, 14 and 15). Indeed, both in the field

and the laboratory, the following infiltration–drainage cycle did not exhibit any

measurable phase drops.

The second point suggests that, for this particular soil, a characteristic size of water-filled

pores might exist, above which the phase drop vanishes. This characteristic size, rc, can be

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bounded by two others, rmin and rmax, which are respectively the smaller pore radius value

estimated from the first infiltration-drainage cycle (exhibiting a phase drop) and the higher

pore radius value estimated from the second infiltration-drainage cycles (with no phase drop):

rmin < rc < rmax, (11)

Both bounds can be quantified from the Jurin equation:

iw hg

cosTr

2 (12)

where T is surface tension (=0.075 N/m for an air-water interface), w is density of water,

g is the gravitational acceleration, is the angle contact (taken equal to 0, in our case) and hi is

the matric potential measured prior to the application of the rainfall during the first

infiltration-drainage cycle (to calculate rmin) or during the second infiltration-drainage cycle

(to calculate rmax). To obtain the narrowest interval in the inequality (11), the tensiometer

values from the field experiment were preferred since they provided the lowest initial matrix

potential (the smaller pore radius) in the first infiltration-drainage cycle and the highest initial

matrix potential (the highest pore radius) in the second infiltration-drainage cycle.

By using equation (12) and the field results (figured 6 and 9), the parameters rmin and rmax

are respectively 14 m (hi =-1.1 m) and 43 m (hi =-0.35 m), respectively. Consequently, the

corresponding pore diameter range is about [30-85 m]

An interesting point arises from this estimation: this estimated range can be referred to as

the pore size of mesopores [30-75 m], in accordance with the Soil Science Society of

America’s terminology (Table 2). Although the class limits given in Table 2 are necessarily

somewhat arbitrary, this estimated range of [30-85 m] also corresponds to the normally

draining pores (or transmission pores) [Greenland, 1981; Kay and Angers, 2000] or to

structural pores [Stengel, 1979]. Consequently, this statement strongly suggests that the

measured phase drop is related to the transition of the water filling of mesopores or structural

pores. In the following, the term “structural pores” is used since it covers a broader class of

transmission draining pores (see Table 2).

Nevertheless, at this stage, an important question remains: what is the physical origin of

this phase drop that occurs as the water fills the structural pores? This question can also be

reformulated by two others: Is the observed phase drop associated with a polarization

mechanism? If so, among the different polarization mechanisms described previously, what is

the relevant process?

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To answer these questions, it may be relevant to express our results in terms of complex

permittivity or complex conductivity *. As previously shown in experimental works

[Chelidze et al., 1999; Slater and Glaser, 2003; Ulrich and Slater, 2004], polarization

magnitude is primarily included in the imaginary part ’’ (or in the real part ’eff) whereas the

complex path of charge carriers in porous materials, i.e., charge transfer phenomena, is related

to the real part ’ (or in the imaginary part ’’eff). In other words, the complex resistivity *

and especially the phase , are not direct measurements of polarization. In fact, as shown in

equation (8), the phase almost defines the polarization magnitude relative to the conduction

magnitude.

Figures 20 and 21 show the evolution of the imaginary part ’’ and the real part ’ of the

complex conductivity measured in the field and the laboratory for the 1.5 kHz frequency.

Both figures confirm that the phase drop is clearly due to a decrease in the imaginary

component ’’ i.e., a decrease in soil polarizability as the infiltrated water filled the structural

pores.

Since the phase drop is not related to the filling of micropores and is enhanced at high

frequencies, it is safe to assume that the underlying polarization process associated with the

phase drop is not purely electrochemical in relation with the EDL but rather a GI polarization.

As far as a GI mechanism is concerned, the simplest depolarization effect related to the phase

drop is a two-step process (Figure 22):

1. Before the arrival of the wetting front (stage 1 in Figure 22), water is mainly in the

microporosity. The wet aggregates associated with the fine fraction of the soil

generate a significant polarization magnitude whose physical origin is likely

complex (i.e., combination of GI and EDL effect) and will not be discussed in

detail here. Nevertheless, it is easy to imagine that during the application of an

external electrical field, the interfaces between the wet aggregates and the

interaggregate pores filled with air would constitute electrical barriers in which a

significant amount of electrical charge carriers would be blocked, leading to the

polarization of the wet aggregates.

2. The fresh water fills the structural pores bypassing the wet polarized aggregates,

leading to a decrease in the bulk polarization amplitude (stage 2 in Figure 22).

This process can be enhanced by the release of a large part of the charge carriers

blocked in the aggregates by diffusion in the water-filled structural pores.

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This kind of Maxwell-Wagner effect (decrease in bulk polarizability due to filling of

structural pores) can be illustrated by a simple calculation based on a MWHB model. In this

approach, the polarized wet aggregates composed of the soil fine fraction and the micropores

(with possibly smaller pores) are modeled as oblate inclusions alternatively embedded in air

(stage 1) and in fresh water (stage 2). The complex conductivity of the soil * corresponding

to both stages is calculated from equation (9) (MWHB model) expressed in complex

conductivities:

ag

m/*

w,a

*

w,a

*

ag

*

agd

*

*1

1

(13)

where dag is the volumetric fraction of aggregates; *

w,a is alternatively the complex

conductivity of air (stage 1) or water (stage 2); *

ag is the complex conductivity of the wet

polarized aggregates that is considered as a fitting parameter since the polarization

mechanisms related to the sole aggregates will not be discussed. As in Samstag and Morgan

[1990], the imaginary part ,,

ag of the aggregates was estimated from the literature by

assuming that the dielectric behavior of the aggregates with microporosity is similar in order

of magnitude to that of a clay-rich rock with a very small structural porosity (i.e., argillite).

The range of values of parameters *

w,a and *

ag is given in Table 3. The results of a

sensitivity analysis (not shown) demonstrated that a change in +/- 50 % of the ,,

ag value

given in Table 2 had a low effect on the soil bulk imaginary conductivity. The particle shape

factor (often called “cementation exponent”) for all inclusions m in equation (13) is taken to

be equal to 2 [e.g., Rhoades et al., 1976; Revil et al., 1998].

A numerical application of this modeling approach is given in Figure 23 for two high

frequencies, 1500 Hz and 150 Hz. The real conductivity of the aggregates has been chosen to

be two-fold higher than the real conductivity of water. The volumetric fraction of wet

aggregates has been chosen in the range of 60-90 % since the structural porosity is typically in

the range 10-40 % in clay loamy soils [e.g., Stengel, 1979].

The results in Figure 23 clearly show a drastic decrease in the soil imaginary conductivity

between the two stages (before and after structural pore filling) for a frequency of 1.5 kHz.

Compared to the experimental decrease, this calculated decrease is possibly overestimated by

the underlying simplifications used in the model: in reality, from stage 1 to stage 2, charge

carriers can also be transferred efficiently by diffusion in the water-filled structural pores and

between aggregates, which may contribute to lowering the bulk polarizability. These aspects

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are not rigorously taken into account in the modeling process. Nevertheless, despite the

uncertainties included in the calculations, this model is in agreement with the experimental

trend; the drastic modeled decrease could explain quantitatively the phase drop observed in

the field and in the laboratory.

Moreover, one may wonder whether the MWHB equation is able to model the frequency

dependence of the measured electrical properties. In other words, can this equation show that

the observed phase drop is enhanced in the high part of the used frequency range? To answer

this question, one has to introduce into the model a relationship between the electrical

properties of aggregates and the frequency: indeed, there is no reason to suppose that the

electrical properties of aggregates do not depend on frequency. Unfortunately, this

relationship is unknown and is a priori difficult to obtain. However, a value of the relative

dielectric permittivity of aggregates equal to 108 at 150 Hz (Table 3), which is not an unusual

value for dense clayey rocks at low frequencies [e.g., Comparon, 2005; Cosenza et al., 2007],

leads to obtaining a lower phase drop compared to that calculated at 1500 Hz (Figure 23).

Although this calculation is not a validation of the proposed model, it confirms the

experimental trend i.e., the decrease in the observed phase drops with frequency. At this

stage, we are aware that further experimental and theoretical investigations are required to

fully validate this approach with regard to the frequency-dependent phenomena observed. In

particular, we need to understand and to model the low frequency electrical spectra of highly

clayey materials.

6. Conclusion

In situ and laboratory experiments were undertaken to estimate the capabilities of the SIP

method to characterize vertical flows in the vadose zone during water infiltration. These

experimental investigations had two original features: (a) they were performed in the same

silty clay loamy soil and (b) they coupled SIP and tensiometer measurements.

During both experiments, the evolution in phase variation showed a significant drop at

high frequencies (typically greater that 1 kHz) during the first infiltration cycles. These phase

drops were correlated to the water filling of pores whose equivalent diameters were estimated

to be in the range of [30-85 m]. This range might be related to structural porosity in this

fine-grained soil.

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These phase drops were qualitatively and quantitatively interpreted as a GI mechanism,

i.e. the decrease in polarization amplitude is mainly due to the filling of a conducting liquid in

the structural pores between high polarized and wet aggregates.

This work strongly suggests the need for further experimental and theoretical

investigations in two directions. Firstly, from a practical point of view, the SIP method seems

to be able to monitor the filling of drainage pores and possibly in the field, thus providing

indications about soil structural features. However, further field work is needed in different

sites and other hydrological situations to validate this capability. Secondly, from a

fundamental point of view, there is still no comprehensive understanding of the polarization

mechanisms involved at the different pore scales (from micropores to macropores) so the SIP

method cannot yet be used efficiently in the field. This is why theoretical investigations on the

fundamental polarization mechanism that occurs in earth materials must remain an active field

of research.

Acknowledgements. This research was supported by the Agence Nationale de la

Recherche (ANR) –ECCO programs (POLARIS II Project: “Polarisation Provoquée

Spectrale” – Spectral Induced Polarization and «Flux d’infiltration, recharge et hétérogénéité:

une approche multi-échelle de la colonne à la parcelle» project n° 161 ACI ECCO 2003).

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References

Binley, A, and A. Kemna (2005), DC resistivity and Polarization methods, in:

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Captions

Table 1 Main mean (n=2) characteristics of the soil for the 30 cm upper layer. Corg =

content of organic carbon.

Table 2. Pore size classification and corresponding functional descriptions (Soil

Science Society of America, 1997, from Kay and Angers, 2000; modified from Greenland,

1981).

Table 3. Typical range of values for the complex electrical conductivity of the three

phases (air, water and aggregates). The parameters ’ag and ’’ag are estimated from the

literature by assuming that the dielectric behavior of the aggregates is similar to that of a clay-

rich rock.

Figure 1. Electrical polarization mechanisms. (a) Electrical Double Layer (EDL)

polarization. The figure illustrates excess and deficiency in ion concentration around a

polarized particle. Dotted line indicates the local diffusion flows of both cations and anions;

dashed line gives the local diffusion flows near the solid surface. (b) Membrane polarization.

Clay particles at pore throats constitute ion-selective zones. The EDL is not drawn for clarity.

(c) Polarization associated with pore throats. Pore throats with corresponding EDL constitute

ion-selective zones. The EDL is not drawn for clarity. (d) No interfacial polarization: the

layered medium is parallel to the electric field; (e) Maxwell (interfacial) polarization: the

layered medium is perpendicular to the electric field; (f) Wagner (interfacial) polarization.

Dielectric host with conductive inclusions.

Figure 2. Schematic view of the field experimental set-up. A. Cross-section B. Top

view.

Figure 3. Schematic view of the experimental procedure.

Figure 4. Matric potentials measured in 6 tensiometers (T1 to T6) vs. time during Test

1. Time 0 corresponds to the beginning of the rainfall event of Test 1. The arrow indicates the

arrival time of the wetting front at the tensiometer.

Figure 5. Arrival time for the wetting front observed for the 12 tensiometers located 8

cm deep (6a) and 13 cm deep (6b).

Figure 6. Mean matric potential at two depths (8 cm and 13 cm) vs. time (Test 1). The

beginning and the end of rainfall application are also shown. The arrow indicates a

152

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characteristic event which is compared to SIP measurements (see Figures 7 and 8). Typical

errors bars are also given.

Figure 7. Resistivity amplitude spectra vs. time (Test 1). The beginning and the end of

rainfall application are indicated by dashed lines. Note that at about time 145 minutes, a larger

spectrum (from 91 mHz up to 12 kHz) was measured.

Figure 8. Phase spectra vs. time (Test 1). The beginning and the end of rainfall

application are also given. For clarity, the spectra below 187.5 Hz are not numbered. Typical

errors bars are also given. The phase drop indicated by an arrow is related to the average time

for the wetting front to reach a steady state (see Figure 6).

Figure 9. Mean matric potential at two depths (8 cm and 13 cm) vs. time (Test 2). The

beginning and the end of rainfall application are also given.

Figure 10. Resistivity amplitude spectra vs. time (Test 2). The beginning and the end

of rainfall application are also indicated by dashed lines. For comparison, the same scale of

amplitude used in Figure 7 has been used.

Figure 11. Phase spectra vs. time (Test 2). The beginning and the end of rainfall

application are also given. For clarity, not all the spectra are numbered. For comparison, the

same scale of phase used in Figure 8 has been used. Typical error bars are also given.

Figure 12. Schematic diagram of laboratory column in (a) section and (b) plan view

(not to scale). Distance of tensiometer from soil surface is given in brackets.

Figure 13. Schematic view of laboratory experimental procedure.

Figure 14.Tensiometer values at three depths (4 cm, 7 cm and 10 cm) vs. time (Cycle

1). At time 0, the rainfall rate was applied. The end of rainfall application is also indicated by

a dashed line.

Figure 15.Tensiometer values at three depths (17 cm, 20 cm and 23 cm) vs. time

(Cycle 1). At time 0, the rainfall rate was applied. The end of rainfall application is also

indicated by a dashed line.

Figure 16. Resistivity amplitude spectra vs. time (1st infiltration-drainage cycle). The

beginning and the end of rainfall application are indicated by dashed lines. The time related to

the seepage at the bottom of the column is indicated by an arrow.

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Figure 17. Phase spectra vs. time (1st infiltration-drainage cycle). The values of the

tensiometer located at the same depth (7cm) are also given. C2 The beginning and the end of

rainfall application are indicated by dashed lines. The time related to the seepage at the

bottom of the column is indicated by an arrow. Typical error bars as a function of frequency

are also given.

Figure 18. Resistivity amplitude spectra vs. time (2nd infiltration-drainage cycle). The

beginning and the end of rainfall application are indicated by dashed lines. The time related to

the seepage at the bottom of the column is indicated by an arrow. For comparison, the same

scale of amplitude used in figure 17 has been used.

Figure 19. Phase spectra vs. time (2nd

infiltration-drainage cycle). The beginning and

the end of rainfall application are indicated by dashed lines. The time related to the seepage at

the bottom of the column is indicated by an arrow. Typical error bars as a function of

frequency are also given.

Figure 20. Imaginary conductivity vs. time for field and laboratory experiments

measured for a high frequency (1.5 kHz) (1st infiltration-drainage cycle). The times

corresponding to the observed phase drop are indicated by arrows.

Figure 21. Real conductivity vs. time for field and laboratory experiments measured

for a high frequency (1.5 kHz) (1st infiltration-drainage cycle). The times corresponding to

the observed phase drop are indicated by arrows.

Figure 22. Schematic describing the two physical conditions (stages) related to the

observed phase drop. The first stage corresponds to the condition before the arrival of the

wetting front - in other words - before the water filling of the mesopores (pores typically

greater than 30 m). At this stage, water is located in the microporosity inside the polarized

aggregates. Charge carriers are blocked in the aggregates since the air is electrically an

isolator. The second stage represents the physical condition after the arrival of the wetting

front: the mesopores are now filled with connected fresh water, leading to a decrease in the

polarizability of the aggregates.

Figure 23. Calculated imaginary soil conductivity as a function of volumetric

aggregate content. Both stages 1 and 2 (before and after the arrival of the wetting front) are

considered.

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Tables

Table 1

% Clay

(g g-1)

% Silt

(g g-1)

CEC

(cmol kg-1)

Ca++

(cmol kg-1)

Na+

(cmol kg-1)

Mg++

(cmol kg-1)

K+

(cmol kg-1)

Corg

(g kg-1)

34.5 54.0 11.9 39.5 0.72 1.52 0.5 14.4

Table 2

Class Class limit (equivalent

pore diameter) ( m)

Functional description

Macropores > 75 Structural

Pores Mesopores 30-75

Normally draining

pores

Transmission

pores

Micropores 5-30 Slowly draining pores

Ultramicropores 0.1-5 Useful water retention

capacity

Storage pores

Cryptopores < 0.1 Non useful water

content

Residual pores

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Table 3

Complex electrical

conductivity

Range (S/m) References and comments

Air

’a= ’’a= 0

Water

’w 9.3 10-2

Measured at 20 °C

’’w 7. 10-6

(f=1500 Hz)

3.5 10-6

(f=750 Hz)

The imaginary part ’’w is calculated

from the relative permittivity of

water i.e. 80: 802 0fw

'' where f

is the frequency; 0 is the free space

permittivity equal to 8.85 10-12

F/m.

Aggregates

'’ag 8.5 10-4

( ’ag =104)

(f=1500 Hz)

8.5 10-1

( ’ag =108)

(f=150 Hz)

The corresponding real relative

dielectric permittivity is also given

’ag

Comparon (2005), Cosenza et al.

(2007)

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Figures

(a) (b)

(c) (d)

(e) (f)

Figure 1

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A M N B

Rainfall simulator

Cover against wind 12 tensiometers at depth 8 cm

Switching boxto tensiometers

12 tensiometers at depth 13 cm

Electrodes

Transmitter

ReceiverControlUnit PC

Optical fibercable

Switching box

A

runoff

Z

Y

X

Datalogger

L=0.99 m

Tensiometer z=0.08 m

Tensiometer, z=0.13 m

A

M

N

B

Electrode

T12

T11

T10

T09

T08

T07

T06

T05

T04

T03

T02

T01

T18

T17

T16

T15

T14

T13

T24

T23

T22

T21

T20

T19

PVC jacket

runoff

Z

Y

X

Datalogger

L=0.99 m

Tensiometer z=0.08 m

Tensiometer, z=0.13 m

A

M

N

B

Electrode

T12

T11

T10

T09

T08

T07

T06

T05

T04

T03

T02

T01

T18

T17

T16

T15

T14

T13

T24

T23

T22

T21

T20

T19

PVC jacket

Figure 2

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0 2 4 6 8 10 12 14 16 18 20 22 24 26 28 30 32 34 36 38 40

Time (hours)

Tensiometers

SIP measurements

Rainfall (15.4 mm/h) Rainfall (32.4 mm/h)

SIP measurements

Test 1 Test 2

Figure 3

-25 0 25 50 75 100 125 150 175 200Time (min)

-4

-3.5

-3

-2.5

-2

-1.5

-1

-0.5

0

Ma

tric

pote

ntial (m

)

T1 (8 cm)

T2 (13 cm)

T3 (8 cm)

T4 (13 cm)

T5 (8 cm)

T6 (13 cm)

Figure 4

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Figure 5

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-20 0 20 40 60 80 100120140160180200Time (min)

-1.2

-0.8

-0.4

0M

atr

ic p

ote

ntia

l (m

)Applied Rainfall rate

StoppedRainfall rate

8 cm

13 cm

Figure 6

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-20 0 20 40 60 80 100 120 140 160 180 200Time (min)

16

20

24

28

32A

mp

litu

de

(O

hm

.m)

Applied rainfall rate

Stopped rainfall rate

fmin= 91 mHz

fmin= 1.46 Hz

fmax= 12 kHz

Test 1

Figure 7

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-20 0 20 40 60 80 100 120 140 160 180 200

Time (min)

0

5

10

15

20

25

-Pha

se (

mra

d)

Appliedrainfall rate

Stoppedrainfall rate

12 kHz

6 kHz

3 kHz

1.5 kHz

750 Hz375 Hz

187.5 Hz

Test 1

1.46 Hz

Figure 8

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-20 -10 0 10 20 30 40 50 60 70 80

Time (min)

-1.2

-1

-0.8

-0.6

-0.4

-0.2

0

Ma

tric

po

ten

tia

l (m

)StoppedRainfall rate

Applied Rainfall rate

Test 2

13 cm

8 cm

Figure 9

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-20 -10 0 10 20 30 40 50 60 70 80

Time (min)

16

20

24

28

32

Am

plit

ude (

Ohm

.m)

StoppedRainfall rate

0.732 HzTest 2

12 kHz

Applied Rainfall rate

Figure 10

-20 -10 0 10 20 30 40 50 60 70 80

Time (min)

0

5

10

15

20

25

-Pha

se

(m

rad)

Applied Rainfall rate

StoppedRainfall rate

12 kHz

6 kHz

3 kHz

Test 20.732 Hz

Figure 11

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Figure 12

0 2 4 6 8 10 12 14 16 18 20 22 24 26 28 30 32 34 36 38 40

Time (hours)

Tensiometers

SIP measurements

Rainfall (15 mm/h) Rainfall (15 mm/h)

SIP measurements

Figure 13

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0 100 200 300 400 50050 150 250 350 450

Time (min)

-5

-4

-3

-2

-1

0M

atr

ic p

ote

ntia

l (m

)

Cycle 1 -Upper part

C1 (4 cm)

D4 (4 cm)

C2 (7cm)

C3 (10cm)

D3 (10cm)

0 20 40 60

-5

-4

-3

-2

-1

0

Stoppedrainfall rate

Figure 14

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0 100 200 300 400 50050 150 250 350 450

Time (min)

-6

-4

-2

0

-5

-3

-1

Ma

tric

po

ten

tia

l (m

)Cycle 1 -Lower part

C4 (17cm)

D2 (17cm)

C5 (20cm)

C6 (23cm)

D1 (23cm)

0 20 40 60 80

-6

-4

-2

0

Stopped RainfallRate

Figure 15

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0 40 80 120 160 200 240 280

Time (min)

32

36

40

44

48

52A

mp

litu

de (

Oh

m.m

)

Cycle 1

93.5Hz

187Hz

1.5kHz

Applied Rainfall rate

Stopped Rainfall rate

Seepage

Figure 16

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0 40 80 120 160 200 240 280

Time (min)

0

5

10

15

20

25

-Ph

ase (

mra

d)

-6

-4

-2

0

Ma

tricp

ote

ntia

l(m

)Cycle 1

93.5 Hz

187 Hz

1.5 kHz

Tensiometer C2

Stopped Rainfall rate

Applied Rainfall rate

Seepage

Figure 17

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0 40 80 120 160

Time (min)

32

36

40

44

48

52

Am

plit

ud

e (

Oh

m.m

)

Cycle 2

93.5 Hz

187 Hz

1.5 kHz

Applied Rainfall rate

Stopped Rainfall rate

Seepage

Figure 18

0 40 80 120 160

Time (min)

0

5

10

15

-Ph

ase (

mra

d)

Cycle 2

93.5 Hz

187 Hz

1.5 kHz

Applied Rainfall rate

Stopped Rainfall rate

Seepage

Figure 19

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0 50 100 150 200

Time (min)

0

0.001

0.002

0.003

0.004

0.005

0.006

Ima

gin

ary

co

nd

uctivity

'' (d

S/m

)

Field experiment

Laboratory experiment

Phase drop

Figure 20

0 50 100 150 200

Time (min)

0.2

0.3

0.4

0.5

0.6

Rea

l conductivity

' (d

S/m

)

Field experiment

Laboratory experiment

Phase drop

Fig. 21

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Figure 22

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0.6 0.7 0.8 0.9

Volumetric aggregates content

0.0001

0.001

0.01

0.1

1Im

ag

ina

ry s

oil

co

nd

uctivity (

dS

/m)

MWHB model

Stage 1-before wetting front

Stage 2- after wetting front (1500 Hz)

Stage 2 - after wetting front (150 Hz)

Phase drop

1500 Hz

150 Hz

Figure 23

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Effects of drying on the low-frequency electrical properties of Tournemire

argillites

Philippe COSENZA*, Ahmad GHORBANI*, Nicolas FLORSCH*, André REVIL#

* UMR 7619 Sisyphe, Université Pierre et Marie Curie-Paris6, Paris, France #

UMR 6635, CNRS-CEREGE, Université d’Aix-Marseille III, Aix-en-Provence, France.

Abstract: Nearly water-saturated argillite samples (initial water content near 3.4 wt%)

were cored from an undisturbed area of an underground facility of the French Institute for

Radioprotection and Nuclear Safety (IRSN), located at Tournemire (Aveyron, France). These

samples were subjected to the following desiccation path: (a) a desaturation phase during

which the samples were dried at ambient temperature conditions, relative humidity equal to

43 % in average and (b) a heating phase during which the same samples were heated at four

temperature levels from 70 °C up to 105 °C. During both phases, the low-frequency complex

resistivity (0.18Hz- 12 kHz) was recorded by a four-electrodes device.

The amplitude of the complex resistivity was extremely sensitive to water content change. At

the end of the isotherm desaturation phase, it has been multiplied by a factor of 3 to 5. During

the heating phase, the resistivity increased by more than two orders of magnitude compared to

the initial state. The percentage of Frequency Effect shows a low sensitivity to water content

changes during the desaturation stage while it increased by two orders of magnitude during

the heating phase. This results confirms that low-frequency spectral signature is extremely

sensitive to textural changes (i.e., thermal-induced microcracking in this case) that occurred

during heating. Moreover, the complex resistivity of the samples show a strong anisotropy (a

ratio of 10 between both amplitudes measured in the perpendicular directions). The classical

Cole-Cole model can not be used to fit the experimental data obtained in the heating phase. A

generalized formulation of this model is required and was successfully applied to represent

the complex resistivity data.

Keywords: Spectral Induced Polarization, complex resistivity, argillite, drying, microcracks.

Abbreviated title: Drying and SIP of Tournemire argillites.

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1. Introduction

In many industrial countries (such as Belgium, Germany, France, Japan, Spain,

Switzerland) deep argillaceous formations are considered as potential host media for high

level radioactive wastes. This is because clayey geomaterials have the ability to adsorb large

amount of ions and they possess the low permeability required to slow down the percolations

of fluids (e.g. Mitchell, 1993). In France, in order to improve the knowledge of the

containment properties of such formations, two geological sites are currently under study: the

Callovo-Oxfordian argillites of the Paris Basin (e.g., ANDRA, 2005a) and the Toarcian

argillites of Tournemire, in the Southern France (e.g., Cabrera et al., 2001).

For safety assessment of long-term radioactive waste disposals, a critical issue is the

impact of the thermo-hydro-mechanical loading induced by the excavation of deep galleries

and by the exothermic canisters (e.g., Kaluzny, 1990; ANDRA, 2005b). In this framework, it

is desirable to have non-invasive tools in order to determine in situ petrophysical parameters

(like the porosity, the permeability, the water content) and the textural changes that can be

induced by thermal and mechanical induced cracking during the construction and the life of

the underground repository.

Complex resistivity method also named Spectral Induced Polarization (SIP) consists in

measuring both the low-frequency resistivity and the phase shift between the voltage and the

applied current. This is a very promising geophysical method to monitor both water content

and fracturing of argillaceous rocks. Indeed, low-frequency and DC resistivity are often used

to determine the water content of porous materials (e.g., Dannowski and Yaramanci, 1999)

and electrical spectroscopy can be used as an efficient tool to detect fractures (Glover et al.,

1997; Glover et al., 2000; Nover et al., 2000; Heikamp and Nover, 2003). Moreover, recent in

situ investigations in the Mont Terri underground laboratory (Kruschwitz and Yaramanci,

2004) showed that SIP can be qualitatively used to characterize the so-called “excavation

damaged zone” (EDZ) located around the galleries. The EDZ is generated by the excavation

because of the stress and temperature changes and the desiccation of argillites.

Nevertheless, to our knowledge, no extensive experimental SIP investigations has been

performed on argillaceous rocks with a high clay content (typically greater than 30 wt%) in

the low-frequency range, typically 10 mHz to 10 kHz. To our opinion, this is mainly due to

two reasons. On the one hand, the oil and mineral companies were not interested to

investigate the physical properties of shale for a long tine. In the other hand, SIP

measurements in the low-frequency range (typically less than 10 Hz), are difficult to conduct

since they require to remove the spurious electrode polarizations occurring at the boundary

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between the sample and the measuring electrodes (e.g., Vinegar and Waxman, 1984,

Garrouch and Sharma, 1994; Levitskaya and Stenberg, 1996; Carrier and Soga, 1999;

Chelidze et al., 1999). The substitution technique based on electrolytic cells between the

sample and the current electrodes (e.g. Vinegar and Waxman, 1984; Olhoeft, 1985) can not be

used for argillaceous rock as their texture is extremely sensitive to water content and salinity

changes. Moreover, the use of rigid and “nonpolarizing” electrodes with a platinum coating

requires an extremely good sample to electrode contact in order to minimize the

corresponding contact resistance. This contact may be difficult to get and it is well-known

that black platinum electrodes are brittle and easily damaged when clamped against rock

samples (see Levitskaya and Steinberg, 1996).

This is why the first goal of this study is to establish a simple and reliable procedure in

order to measure low-frequency complex electrical resistivity of an argillaceous rock. The

second goal of our study in relation to the monitoring of underground facilities, is to assess

the ability of SIP to measure both water content changes and fracturing. In this purpose, the

desiccation path is preferred, starting with samples close to saturation, cored in the

undisturbed zone of the site. The third objective of our paper concerns the quantitative

modelling of the experimental data. We examine below the simplest models describing the

effects of desiccation on the measured low-frequency electrical properties of the argillites.

2. Geological overview and sampling strategy

The site of Tournemire was chosen as a test site by the French Institute for

Radioprotection and Nuclear Safety (IRSN) to study the confining properties of argillites for

research purpose. This site is located in southern France, in the western border of the Causses

Basin, a Mesozoic sedimentary basin. The general stratigraphy of the Tournemire massif is

sub-horizontal (Figure 1A.). Three major formations are identified. The lower formations

(Hettangian, Sinemurian and Carixian) and the upper formations (Upper Aalenian, Bajocian

and Bathonian) consist in limestones and dolomites. The intermediate formations (Domerian

and Toarcian) correspond to marls and argillaceous rocks. The main geological target of the

studies conducted by IRSN is the upper Toarcian formation corresponding to a layer 160 m

thick of argillites.

The Toarcian formations is intercepted by a set of boreholes and two galleries drilled

from an old railway tunnel crossing the Upper Toarcien (Cabrera et al., 2001) (Figure 1A.).

The mineralogical compositions of samples taken from boreholes shows that clay minerals

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(kaolonite, illite, and interstratified illite-smectite) represent about 40 wt.% of the bulk-rock

composition (De Windt et al. 1998; Charpentier, et al., 2004). The coarse fraction contains

quartz (~20 wt.%), K-feldspars, bioclasts, and pyrite (~2 wt.%). Carbonates (calcite with

minor dolomite and siderite) constitute 15 wt.% of the bulk-rock composition. Geochemical

studies (e.g., Bonin, 1998, De Windt et al. 1998) and mechanical investigations (e.g. Niandou

et al., 1997; Cosenza et al., 2002) confirmed that Tournemire argillite consists in an

transverse isotropic material. Some physico-chemical properties of Tournemire argillites are

given in Table 1.

A set of four samples was taken from the boreholes TM90 and TM180 (Figure 1B.),

which were drilled in 2005 perpendicularly to the wall of the main tunnel. The TM90

borehole is subhorizontal and parallel to the bedding in the Toarcian formation and TM180

was drilled vertically in the same formation perpendicularly to the tunnel axis. This

configuration allow to investigate the degree of anisotropy of this material. The drilling was

carried out with air to avoid any contact of the formation with any kind of aqueous solutions.

Samples were immediately taken after the completion of drilling and put in Al-coated plastic

bag under confined N2 atmosphere. The samples were located between 12 and 14 meters from

the gallery wall in a preserved zone outside the so-called Excavation Disturbed Zone (EDZ)

and outside the influence of the ambient air. The samples have been cored far from the wall of

the tunnel wall in order to study near-saturated and undamaged argillite samples. This state

corresponds therefore to an initial reference state (IRS). In a first stage, in order to understand

separately the impact of water content changes and fracturing, it was easier to work with this

IRS and not to mix the effects of various (hydraulical and mechanical) processes existing in a

material located in the EDZ.

The geometrical features of the samples and their water content are given in Table 2.

The low values of water content (3.33 wt.% in average) are typical of this argillite in a natural

state (Bonin, 1998). From the variation ranges of the porosity and the grain density given in

Table 2, we checked that this average corresponds to a near-saturated state, between 90 % and

100% of saturation degree.

3. Methodology

3.1. Experimental set-up

The SIP FUCHS-II measure the complex resistivity over 7 decades of frequency (1.4

mHz up to 12 kHz). It consists in two remote units that record the current I and voltage U

signals (Figure 2).

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The complex impedance Z* is defined by (e.g., Pelton et al., 1983):

)()(*)(* ieZI

UZ (1)

where (i2=-1); )(*Z and )( are the impedance amplitude and the phase

respectively. They are a priori function of the angular frequency . The existence of the

phase )( results from polarization processes occurring in the sample, i.e. the so-called

Induced Polarization (IP) effect.

To measure the whole spectrum, the SIP FUCHS-II apparatus starts with the highest

frequency, 12 kHz, and the N other decreasing frequencies are obtained by the following

division: 12 kHz/2N. Optical fibres are used in order to minimize electromagnetic cross-

couplings between the transmitter and the receiver. The measured data are transferred to the

base unit, where the apparent resistivity and the phase shift are determined. The SIP FUCHS-

II is connected to a computer, to record the data and to display the results in real-time.

As mentioned previously, the main difficulty at low frequency is to avoid two spurious

effects that interact each other: (a) the disturbing impedance of the electrode-sample contact

and (b) the so called “electrode polarization” associated with electrochemical reactions

occurring at the electrode-sample boundary (e.g., Vanhala and Soininen, 1995; Levitskaya,

and Stenberg, 1996; Chelidze et al., 1999).

To minimize these effects in a simple way, measurements have been performed with a

four-electrode device using low-cost medical electrodes. The potential (or measuring)

electrodes and the current (or source) electrodes are electrocardiogram (ECG) Ag/AgCl

electrodes (Asept Co.) and thin carbon films (Valutrode® electrodes from Axelgaard

Manufacturing Co.), respectively. Silver-silver chloride (Ag/AgCl) electrodes which are

known to be stable almost non-polarizable in comparison with metal electrodes are widely

used in laboratory SIP measurements (e.g. Vinegar and Waxman, 1984; Vanhala and

Soininen, 1995). In our study, ECG Ag/AgCl electrodes consists of a small metal round piece

(10 mm diameter) galvanized by silver and covered with a soft sponge imbibed of a AgCl gel.

The carbon films (50 mm diameter, 1 mm thick), that are used in electrotherapy are circular

and covered with a conductive adhesive gel which provides a good electrical contact between

the electrodes and the rock sample (i.e., no air gaps in between).

Our four-electrode device was validated using porous and electrically inert samples. We

chose “clean” limestone samples. Indeed, “clean” (i.e. with no clay fraction) limestone

saturated with a highly-conductive brine will not generate spurious polarization (e.g., Van

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Voorhis et al., 1973; Vinegar and Waxman, 1984). Figure 3 shows the resistivity and the

phase spectrum in the range 0.18 Hz -12 kHz of two limestone samples from Lavoux and

Vilhonneur. They were characterized by low clay fractions typically less than 1 wt%, (Bemer

et al., 2004) saturated with a 0.1 .m brine (NaCl) conductivity. No significant polarization

has been measured in the frequency range 0.18 Hz to 12 kHz except for the highest frequency

value of 12 kHz for which a small but significant phase shift is observed and likely associated

with an electromagnetic coupling/noise effect. The existence of this phase shift implies a

small error of about +/- 1 mrad on the measurements for frequencies greater than 6 kHz. For

lower frequencies, the phase shift is less than +/- 0.5 mrad that is a typical error value for the

SIP-Fuchs (e.g. Weller et al., 1996; Binley et al., 2005).

In fact, following the experimental configuration given in Figure 2, and in order to

compare the data from the different samples (with different geometries), a geometrical factor

K (expressed in meters) has to be calculated in order to convert the measured complex

impedance Z* as complex resistivity *:

*( )= K Z*( ) (2)

The parameter K has been calculated numerically by solving the Laplace equation with a

finite-difference scheme. Its value for each sample is given in Table 1. It should be noted that

)(* will be called hereafter the amplitude of the complex resistivity.

3.2 Experimental procedure

The samples were monitored during two phases. In the first phase, called below the

“desaturation phase”; the samples were dried at ambient temperature conditions. In the second

phase, called below the “heating phase”, the same samples were heated at four temperature

levels (70, 80, 90 and 105 °C).

The desaturation phase provides a desiccation path with samples that are initially nearly

water-saturated. It can also mimic the effect of ventilation in an underground gallery. During

this phase, different parameters were recorded over time (up to one hour to four days) as a

function of the dehydration rate. These parameters are the loss of weight induced by

desiccation, the complex resistivity spectrum (phase and amplitude) in the frequency range

0.18 Hz-12 kHz, the relative humidity (RH%), the room temperature and the temperature of

the surface of the sample by a non-contact thermometer. The desaturation phase was

considered as finished when the sample weights did not evolve anymore; it lasted from 19 to

22 days.

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The heating phase was started immediately after the end of the desaturation phase. The

same set of samples was subjected to four background temperature levels by an oven: 70 °C,

80 °C, 90 °C, and 105 °C. At each level, temperature was maintained constant during 24

hours. The last temperature level (105 °C) allowed to measure the initial water content on the

basis of the loss of weight of the samples. Before and after each temperature level, the loss of

weight and the complex resistivity spectrum were measured. It should be noted that the

dielectric spectrum was not recorded immediately after removal from the oven but at least 5

hours afterwards, in order to obtain a thermal equilibrium, i.e., to equilibrate sample

temperature and room temperature.

There were several goals that we pursue by doing the measurements during the heating

phase. They are (a) to provide some physical insights concerning the effect of temperature

induced by exothermic nuclear wastes on the dielectric behaviour of argillite, (b) to remove a

significant part of the “bound” water in the microporosity, (c) to generate microcracks in the

samples. These microcracks are formed in response to two processes. First, heating is

responsible for local thermal stresses in the different components (the different minerals and

the interstitial liquid). In turns, these thermal stresses induces local thermal strain

incompatibilities and hence microcracks. In addition, the cooling of the sample after their

removal from the oven generates a high tensile stress (e.g., Bérest and Weber, 1988), which

may go beyond the low tensile strength of the argillaceous rock, typically in the range of 2-10

MPa (e.g., Rousset, 1988).

4. Results and qualitative interpretation

4.1 Loss of weight under desiccation

Figures 4a and 4b show the evolution of the water content during both phases

(desaturation and heating) for each sample. As mentioned previously, the duration of the

desaturation phase was ranging from 19 days (TM90-1260) up to 27 days (TM180-1288). The

samples with the same size and from the same borehole (i.e., TM90-1260 and TM90-1280)

show similar dehydration rates during the desaturation phase (Figure 4a). During this phase,

the relative humidity was equal to 43 % in average. This corresponds to a rather dry

atmosphere. Despite of this low value of relative humidity, the desaturation induced a limited

loss of weight for the whole set of samples. Indeed, they kept the half of their initial water

content (between 48 % and 54 %, see Figures 4a and 4b) at the end of this phase.

Consequently, it is suspected that this desaturation phase involved mainly the water removal

from the macro and mesoporosity (typically for pore sizes the range 0.8 nm up -50 nm, see for

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instance Rouquerol et al., 1994) and hence moderate textural changes. Indeed, if an adsorbed

water layer of thickness dw surrounding platy particles is considered, the corresponding water

content w is proportional to the specific surface Sa, as follows (e.g., Mitchell, 1993):

wwa dSw (3)

where w is water density. By using the approximate equation (3), a mean value of Sa equal to

26 m2/g, measured by the BET/N2 method on Tournemire argillite (Bonin, 1998; Devivier et

al., 2004) and a value of dw equal to 0.8 nm (about two diameters of H2O molecules) give a

value of water content associated with microporosity equal to 2.1 %. This order of magnitude

is confirmed by the results of others experimental studies performed on the same material

(Valès et al., 2004). Furthermore, it should be emphasized that the water content calculated on

the basis in a drying oven at 105°C leads to underestimate the real water content in argillite.

Indeed, a drying at 105°C during 24 h does not remove all the water, specially “bound” water,

in smectite clays (e.g., Tessier, 1978).

During the heating phase, the small “rebounds” observed in the figures 4a and 4b are related

to the removal of the samples from the oven in order to return to a thermal equilibrium with

the room.

4.2 Effect of drying on amplitude spectra

Amplitudes obtained during both experimental stages (desaturation and heating phase) at two

extreme frequencies (0.18 Hz and 12 kHz) are presented in Figures 5a and 5b as a function of

water content.

Considering the desaturation phase, comparatively to the initial near-saturated state,

amplitudes of samples TM 90 and TM 180 boreholes were multiplied by a factor 3 and 5,

respectively. This result demonstrates that DC or low-frequency electrical methods are very

promising to monitor the evolution of water content. In addition, the anisotropic texture of

argillite influences significantly the electrical properties. Indeed, figure 5a and figure 5b show

that there exists about one order of magnitude between the amplitude parallel to the

stratification and that perpendicular to the stratification. Nevertheless, we are aware that this

strong contrast may be lower in the field since electrical properties, as for many other physical

properties are stress dependent (e.g., Glover et al., 1997). Indeed, the core decompression

during the drilling may induced a small but significant opening of some natural bedding

planes in the samples (e.g., Niandou et al., 1997).

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Moreover, considering the desaturation phase, results show that the relationship

between amplitude * and the water content w is slightly frequency-dependent. This result

is also illustrated in Figure 6 where the amplitude spectrum of sample TM 90-1280 is plotted

at different values of water content. On the basis of the discussion given in the previous

section, this suggests that the loss of free water from macroporosity does not generate

significant distortion of the low-frequency amplitude spectrum. Furthermore, an amplitude

spectrum measurement will not provide any significant additional insights in regard to in situ

monitoring of water content.

During the heating phase, the amplitude increases drastically by 2 to 3 orders of

magnitude when the background temperature increases. Consequently, the thermal-induced

microcracking and the loss of a significant part of “bound” water in the microporosity affect

significantly the amplitude spectrum of the complex resistivity (Figure 6). This can be shown

by using the percentage of frequency effect, pFE, (e.g., Van Voohris et al., 1973)

)12(*

)12(*)18.0(*(%)

kHz

kHzHzpFE , (4)

where )18.0(* Hz and )12(* kHz are the amplitudes measured at the two extreme

frequencies (0.18 Hz and 12 kHz). The parameter pFE is plotted in Figure 7 as a function of

water content. The results illustrate clearly the previous observations given in Figures 5a, 5b,

and 6, the pFE remains low and almost constant during the desaturation phase (i.e,. no change

in amplitude spectrum) while it increases drastically during the heating phase. Consequently,

this parameter could be used to discriminate the evolution associated with free water and that

with microcracking.

At this stage, it is difficult to identify clearly the polarization processes related to the

values of pFE measured during the desaturation phase. When clay minerals are present in a

sedimentary rock, several researchers have consider that SIP is explained by the “membrane

polarization” model, for which the sediment is described by two zones: selective and non-

selective domains, which are connected in series (Marshall and Madden, 1959; Klein and Sill,

1982; Vinegar and Waxman, 1984; Titov et al., 2002). Following this model, the zones are

associated with different effective mobilities (or Hittorf transport numbers) of cations and

anions which, under the applied external electrical field, produce local charge accumulations

and charge density gradients that are responsible for the frequency dependence of the

resistivity. However, others polarization processes can be also invoked: the Maxwell-Wagner

effect related to the heterogeneity of the material and macroscopic space charge distributions

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(Olhoeft, 1985) and the polarization of the electrical double layer (see Dukhin and Shilov,

1974; Garrouch and Sharma, 1994; Vanhala, 1997; Revil et al., 1998).

Nevertheless, considering the heating phase associated with much higher values of pFE,

the most appealing explanation is to consider the role of the thermal-induced microcracks as

micro-capacitors contributing to create displacement currents and hence to induce

macroscopically frequency-dependent resistivity measurements. This aspect will be discussed

further.

4.3 Effect of drying on phase spectrum

The phase measured during both experimental stages (desaturation and heating phase) at

two extreme frequencies (0.18 Hz and 12 kHz) are presented in Figure 8a and figure 8b as a

function of the water content.

At the opposite of amplitude measurements, a significant difference in the measured

phases between both samples extracted from the same borehole TM180 (called hereafter

TM180 samples) can be observed. Since this is not the case for both samples taken from

borehole TM90 (horizontally drilled), this difference may be attributed to a small vertical

variation in the mineralogy and/or in the texture. Note that both TM180 samples have

different initial water content (Table 1) and are located at 1424 mm and 1288 mm from the

gallery wall, respectively.

In comparison with amplitude spectra (Figures 5a. and 5b), Figures 8a and 8b indicate

that an evolution of the phase over two decades in the whole range of water content values.

The phase is less sensitive than amplitude to change in the water content. It should be

mentioned that the erratic phase variations for high water content for TM90 samples at 0.18

Hz (Figure 8b) are due to the measurements of low phase values: these values have the same

order of magnitude than the instrumental error.

However, the comparison between the amplitude and phase spectra evidences also some

similar features. Indeed, both parameters show a continuous evolution with water content for

both experimental stages (desaturation and heating) for TM180 samples. At the opposite of

the TM90 samples, no significant discontinuity in the amplitude and phase can be observed at

the desaturation-heating transition. We suggest that this remarkable feature is associated with

the anisotropy of the Tournemire argillite. Indeed, the texture of an argillite is characterized

by two components (e.g., Sammartino et al., 2003) (Figure 9A.): a coarse and non-conducting

phase consisting of grains (mainly tectosilicates and carbonates, in the range of a few dozens

up to few hundreds of micrometers), often aligned sub-horizontally, i.e. perpendicular to the

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compaction and in the other hand, a fine and electrical-conducting fraction, i.e. the clay

matrix in which clay particles (individual and/or aggregates of 2:1 illite, smectite or 1:1

kaolinite units) are also oriented perpendicularly to the compaction (e.g. Djéran-Maigre et al.,

1998). Moreover, scanning electron microscope (SEM) images reveal that a major fraction of

the macroporosity in argillite is located between the coarse phase and the clay matrix

(Sammartino et al., 2003). This explains why voids and microcracks appear primarily around

carbonates and quartz grains when a saturated argillite begins to dry (e.g., Gasc-Barbier et al.,

2000). As the desaturation process evolve, subhorizontal fractures parallel to the stratification

are generated as a result of the coalescence of the initial voids and microcracks in the

anisotropic clay matrix (Figure 9B.). Finally, the heating favours the occurrence of additional

cracks mainly associated with the clay matrix (Figure 9C.).

Consequently, following these simple ideas, the complex resistivity measured

perpendicularly to the stratification (TM180 samples) and thus perpendicularly to the

desiccation-induced fractures are mainly affected by the non-conductive barriers consisting in

these microcracks. The current flow has to face directly the fractures. As a result, the

microfractures which appears in the clay matrix during the heating phase have a more little

influence. At the oposite, the complex resistivity measured parallel to the stratification (TM90

samples) is less influenced by the desiccation-induced microfractures generated during the

desaturation phase since the latter are sub-parallel to the direction of the current flow.

Measurements for TM90 samples will be more sensitive to microcracks in the clay matrix.

This explains why a clear discontinuity in the evolution of SIP parameters is observed in

figures 5a, 5b, 8a, and 8b at the desaturation/heating transition.

5. Representation of Polarization Spectra

5.1 Conventional empirical models

In this section, the conventional empirical models widely used in IP studies are

presented. Our objective is twofold: (1) to invert the data with these conventional models and

(2) to provide a practical model (i.e., with the smallest number of independent parameters) to

characterize the SIP spectra of clayey rocks undergoing drying.

The most popular empirical model is probably the Cole-Cole (CC) model (e.g., Cole and

Cole, 1941; Pelton et al., 1983; Vanhala, 1997):

cim

)(1

111)(* 0 , (5)

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where 0 is the direct-current resistivity ( m) (i.e. 0 when 0 ), m is the

chargeability, c is the Cole-Cole exponent, is a time constant (s); is the angular frequency

(rad/s) and i2=-1. The chargeability m describes the magnitude of the polarization effect while

is related to the position of the phase peak, fc, at which the phase reaches a maximum

(Pelton et al., 1983). This critical frequency is given by:

ccm

f2/1)1(2

1. (6)

In order to represent simply their data, Cole and Cole (1941) chose to represent the real

part Re( *) or ’ and the imaginary part Im( *) or ’’ of the measured complex resistivity *

at each function, by points in the complex plane. This synthetic way to display dielectric data

is now extensively used and some examples are given in Figure 10. With this method of

representation called hereafter Argand representation, the CC model appears as a circular arc

with its center either on or below the real axis of the complex plane (Figure 10).

However, experimental investigations on rock samples have shown in several cases

(porphyry copper deposits, some sedimentary rocks) that complex resistivity data could

appear as a straight line in the Argand plot (Van Voohris et al., 1973; Weller et al., 1996): the

real and imaginary parts obey identical power laws of frequency. Such data are represented

the so-called Drake model, also called the Constant-Phase-Angle (CPA) model. It can be

expressed by the equation:

ai )1(

1)(* 0 , (7)

where only three parameters 0 , and a are unknown. At high frequencies ( >> 1), the

amplitude is given by:

a)()(* 0 , (8)

and the phase is given by:

a2

. (9)

In order to model asymmetrical circular arc in the Cole-Cole representation, the Cole-

Davidson (CD) model has been proposed by Davidson and Cole (Davidson and Cole, 1950)

(Figure 10):

aim

)1(

111)(* 0 (10)

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The CC, CPA, and DC models can be also generalized into a single formulation; the so-

called the generalized, GCC model, (Pelton et al., 1983)

acim

))(1(

111)(* 0 . (10)

When a=1 or c=1, one obtains the CC model or the CD model, respectively. When c=1 and

m=1, the CPA model is obtained. Klein and Sill (1982) showed that the GCC model is the

best model to fit the experimental data obtained from artificial clay-bearing sandstones.

5.2 Inversions of the dielectric spectra

The dielectric spectra have been inverted using a non-linear iterative least-square

method (Tarantola and Valette, 1982) on the basis of the three representation models given

above.

With respect to the desaturation phase, the inversion of the spectra of the TM90 samples

shows that the CC formulation provides the best agreement when the chargeability is fixed

equal to 1 (Figure 11). The inversions of TM180 spectra were a priori more complex: as it is

shown for the example given in Figure 11 (TM180-1424, w=3.49 %), these spectra indicate a

linear element at the lowest part of the frequency range (0.18 Hz-5.86 Hz) i.e., with a

frequency behaviour corresponding to the power–law given by equation (8) ( a ).

Consequently, the most suitable model for the TM180 samples is likely a combination of the

CC model (for the high part of the frequency range) and the CPA model (for the low part of

the frequency range).

Figure 12 illustrates the inversions corresponding to the data of the heating phase. The

best agreement with the dielectric spectra was obtained with the GCC model which can

reproduce the specific asymmetrical arcs observed in the Argand diagram of the complex

resistivity (Figure 12). For both desiccation phases, the evolutions of CC and GCC parameters

as a function of the water content are given in Figures 13a, 13b, 13c 13d and 13e. In these

figures, the TM180 samples are not considered in the desaturation phase since their spectra

could not be modelled by a single CC model.

Figures 13a and 13d show that the parameters 0 and are very sensitive to changes in

the water content. The water content dependence of 0 is not surprising since DC-resistivity is

known to be a good indirect predictor of water content (e.g., Dannowski, and Yaramanci,

1999). However, the water content dependence of is more difficult to explain. This

parameter is often linked to the size of polarizable grains (e.g., Vanhala, 1997). Nevertheless,

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when clay-bearing sedimentary rocks are considered, various formulations (e.g., Madden and

Marshall,1959; Vinegar and Waxman, 1984; Titov et al., 2002; Titov et al., 2004) agree with

the fact that the relaxation time depends on a characteristic length l between two selective

zones following:

2l . (11)

In shaly sands, a selective zone, which corresponds to an accumulation of electrical

charges (i.e., electrical poles) is typically an aggregate of clay minerals or the contact between

two adjacent quartz grains coated by clay particles. This relationship (l) explains also why

Klein and Sill (1982) found a good correlation between values inverted by a CGG model

and the size of isolating beads in their artificial clay-glass beads mixtures.

We suggest that our values confirm these previous theoretical and experimental

studies. As the heating occurs, the average distance between selective zones consisting in

interfaces between shrunk clay matrix and some microcraks, increases due to the growth of

the microcracks and the generation of new microcracks in the medium (Figure 14). The

corresponding electrical tortuosity increases. As a result, the parameter evolves drastically

over five decades following a power-law as given in (11). This process is likely associated

with the generation of new selective zones (i.e. new electrical poles). This is confirmed by the

increase of the chargeability, m with the heating (Figure 13b).

6. Conclusions

Low-frequency dielectric spectra measurements have been conducted on a set of

argillite samples taken from the Tournemire test site, which is under study by the IRSN. The

dielectric spectra have been recorded with samples submitted to the following desiccation

path: (a) a desaturation phase under ambient air and then (b) a heating phase corresponding to

four temperature levels (70 °C, 80 °C, 90 °C, and 105 °C).

This experimental investigation demonstrates (a) the interest of using the SIP method to

remotely monitor both the water content and the thermally-induced microcracks and (b) that

the best models to invert the dielectric spectra is the CC model and the GCC model for the

desaturation phase and the heating phase, respectively. However, the data show that the

development of the anisotropy can induced different spectral signatures and polarization

processes. This may lead to difficulty for the use of a comprehensive model. In this situation,

a complex resistivity tensor should be introduced depending on the fabric tensor of the

medium.

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The next steps of this work would be (1) to improve our knowledge of the underlying

physical process involved in the IP effect of clayey rocks (2) to apply the SIP method in the

field, i.e., in the gallery of a deep repository. Following the first task, as mentioned

previously, the involved physical and chemical processes are complex and numerous: the

membrane polarization effect, the Maxwell-Wagner effect, the polarization of the Electrical

Double Layer. To our opinion, the best way to reach successfully this objective, would be to

use upscaling approaches associated with well-characterized physical processes previously

identified by relevant microscopic observations (SEM etc..).

Acknowledgements. This research was supported by the Agence Nationale de la

Recherche (ANR) –ECCO program (POLARIS Project: “Polarisation provoquée spectrale” –

Spectral Induced Polarization). We thank also Elizabeth Bemer and Jean-François Nauroy of

French Petroleum Institute (IFP) for providing the limestone samples.

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Stress, and Wettability on the Dielectric Properties of Brine Saturated Rocks: 10 Hz to 10

MHz, Geophysics, 59, 6, 909-917.

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Murrell, S. A. F. (1997), Damage of Saturated Rocks Undergoing Triaxial Deformation using

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Glover, P. W., Gomez J. B., and Meredith, P.G. (2000), Fracturating in Saturated Rocks

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Experimental Study, Earth and Planetary Science Letters. 5621, 201-213.

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Kaluzny, Y., (1990), Evaluation de la Sûreté du Stockage de Déchets Radioactifs en

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Klein, J. D., and Sill, W. R. (1982), Electrical Properties of Artificial Clay-bearing

Sandstone, Geophysics, 47, 11, 1593-1605.

Kruschwitz, S., and Yaramanci, U. (2004), Detection and Characterization of the

Disturbed Rock Zone in Claystone with Complex Resistivity Method, J. of Appl. Geophys.,

57, 63-79.

Levitskaya, T.M., and Stenberg, B. K. (1996), Polarization Processes in Rocks 2.

Complex Dielectric Permittivity method, Radio Sci., 4, 781-802.

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Geophysics, 24, 790-816.

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Investigation of the Mechanical Behaviour of Tournemire Shale, Int. J. Rock Mech. Min. Sci.,

34, 3-16.

Nover, G., Heikamp, S., and Freund, D. (2000), Electrical Impedance Spectroscopy

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Resistivity and Dielectric Data, Part I., Geophysical Trans., 29, 4, 297-330.

Revil, A., L., M., Cathles, III, Losh, S. and Nunn, J. A. (1998), Electrical Conductivity

in Shaly Sands with Geophysical Applications. J. Geophys. Res.,103(B3), 925-936.

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Stockage de Déchets Radioactifs, Ph-D dissertation, Paris, Ecole Nationale des Ponts et

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Distribution of Porosity and Minerals in Clay Rocks from the Callovo-Oxfordian Formation

(Meuse-Haute-Marne, Eastern France) – Implications on Ionic Species Diffusion and Rock

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Tarantola, A., and Valette, B. (1982) Generalized Non Linear Inverse Problem solved

using the Least Square Criterion, Rev. Geophys. and Space Phys., 20(2), 219-232.

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Tessier, D., (1987), Etude de l’organisation des argiles calciques. Evolution au cours de

la dessiccation, Ann. Agro., 29, 4, 319-355.

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Experimental Study of Time-Domain-Induced Polarization in Water Saturated Sands, J. Appl.

Geophys., 50, 4, 417-433.

Titov, K., Kemna, A., Tarasov, A., and Vereecken, H. (2004), Induced Polarization of

Unsaturated Sands Determined through Time Domain Measurements, Vadose Zone J., 3,

1160-1168.

Valès, F., Nguyen Minh, D., Gharbi, H., and Rejeb, A. (2004), Experimental Study of

the Influence of the Degree of Saturation on Physical and Mechanical Properties in

Tournemire shale (France), Appl. Clay Sci., 26, 197-207.

Van Voorhis, G. D., Nelson, P. H., and Drake, T. L. (1973), Complex Resistivity

Spectra of Porphyry Cooper Mineralization, Geophysics, 38, 49-60.

Vanhala, H. and Soininen, H. (1995), Laboratory Technique for Measurement of

Spectral Induced Polarization Response of Soil Samples, Geophys. Prospecting, 43, 655-676.

Vanhala, H. (1997), Laboratory and Field Studies of Environmental and Exploration

Applications of the Spectral Induced Polarization (SIP) Method, Ph-D dissertation, Helsinki

University of Technology.

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Geophysics, 49, 9, 1267-1287.

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Captions

Figure 1. A: Geological cross-section of the Tournemire tunnel (modified from

Cabrera et al., 2001). The tunnel is drawn in bold line; the transversal galleries and all the

previous boreholes are not shown. B: Locations of the TM90 borehole and TM180 borehole

(not to scale).

Figure 2. Experimental set-up, RU-0: Remote Unit 0 (or Transmitter); RU-1: Remote

Unit 1 (or Receiver). Note that both remote units are mobile since SIP-Fuchs II equipment is

used for field measurements. ECG P1 and ECG P2: electrocardiogram Ag/AgCl electrodes as

potential electrodes; CF C1 and CF C2: Carbon films as current electrodes.

Figure 3. a. Amplitude spectra of limestone samples. b. Phase spectra of limestone

samples.

Figure 4. a. Loss of weight of samples TM90-1260 and TM90-1280 as a function of

time. b. Loss of weight of samples TM180-1424 and TM180-1288 as a function of time.

Figure 5. a. Amplitude at 12 kHz as a function of water content. b. Amplitude at 0.18

Hz as a function of the water content. The direction of the current flow I comparatively to the

stratification is also shown.

Figure 6. Amplitude spectra of sample TM90-1280 during the desaturation and the

heating phase.

Figure 7. Percentage of Frequency Effect (pFE) as a function of the water content.

Figure 8. a. Phase at 12 kHz as a function of water content. b. Phase at 0.18 Hz as a

function of water content. The direction of the current flow I comparatively to the

stratification is also given.

Figure 9.A. Simplified texture of argillite in the saturated case (modified from

Sammartino et al. 2003). B. Textural evolution during the desaturation phase. In a first step,

microcracks are generated from macropores mainly located at the clay-grain contacts, due to

the shrinkage of the clay fraction. In a second step, these microcracks propagated

subhorizontally into the anisotropic clay matrix. C. Textural evolution during the heating

phase (adapted from Sammartino et al., 2003).

Figure 10. Examples of conventional empirical models displayed in an Argand

representation: Cole-Cole model (with 0=30 .m, =10-2

s, m=0.7, c=0.4); CPA model (with

0=35.5 .m, =105 s, c=0.008), Davidson-Cole model 0=30 .m, =10 s, m=0.8, c=0.13).

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Figure 11. Examples of experimental and modelled dielectric spectra obtained during

the desaturation phase in an Argand diagram.

Figure 12. Experimental and modelled dielectric spectra of TM90-1280 sample

obtained during the heating phase in an Argand diagram. The real and imaginary parts are

normalized by the greatest value taken in each spectrum.

Figure 13. Inverted parameters of the Cole-Cole model and the Generalized Cole-Cole

model as a function of water content. (a) The DC-resistivity 0. (b) The chargeability m. (c)

The Cole-Cole exponent c; (d) The time constant . (e) The exponent a of the Generalized

Cole-Cole model.

Figure 14. Schematic representation of the polarization process during the heating

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Tables

Table 1. Physico-chemical properties of Tournemire (from Bonin, 1998; Cabrera et al., 2001)

Density 2.5-2.6 103 kg.m

-3

Grain density 2.7-2.8 103 kg.m

-3

Pore size centred around 2.5 nm

Porosity 6 –9 %

Gravimetric water content 3.5 – 4 %

Specific surface area 23-29 m2/g

Cation exchange capacity 9.5-10.8 meq/100 g

Hydraulic permeability 10-14

-10-15

m/s (laboratory)

10-11

-10-14

m/s (in situ)

Table 2. Geometrical features and water content of the samples.

Sample Length (mm) Diameter (mm) Water content

(wt. %)

Geometrical

factor (m)

TM90-1280 193 79.5 3.42 0.0848

TM90-1260 205 79.5 3.33 0.0848

TM180-1424 52.5 79.5 3.49 0.1751

TM180-1288 88 79.5 3.09 0.1731

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Figures

N Sm

m

2

3

4

5

6

7

8

TunnelTunnel

Cernon Fault

TM180

TM90

Tunnel

S

N

A

B

1. Hettangian: limestone and dolomite2. Sinemurian: limestone and dolomite3. Carixian: limestone4. Domerian: marls5. Toarcian: argilites and marls6. Aalenian: limestone7. Bajocian: limestone and dolomite8. Bathonian: limestone and dolomite

TM Boreholes

1 m

Tournemire site

0 1000 2000-500 500 1500

200

400

600

800

1000

200

400

600

800

1000

1

Figure 1

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Figure 2

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10-1

100

101

102

103

104

105

Frequency (Hz)

10-1

100

101

Am

plit

ude

(m

)

Brine (0.1 m)

Vilhonneur limestone

Lavoux limestone

10-1

100

101

102

103

104

105

Frequency (Hz)

-10

-8

-6

-4

-2

0

2

4

6

8

10

-pha

se

(m

rad

)

Brine (0.1 m)

Vilhonneur limestone

Lavoux limestone

Figure 3

0 10 20 30Time (days)

0

1

2

3

4

Wa

ter

co

nte

nt

(%)

TM90-1280

TM90-1260

HeatingDesaturation

70 °C

80 °C

90 °C

105 °C

0 10 20 30 40Time (days)

0

1

2

3

4

Wa

ter

co

nte

nt

(%)

TM180-1288

TM180-1424

TM90-1260:

HeatingDesaturation

70 °C

80 °C

90 °C

TM180-1288:

105 °C

Figure 4

(a) (b)

(a) (b)

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0 1 2 3 4Water content (%)

100

101

102

103

104

105

106

Am

plit

ude (

m)

Frequency: 12 kHzTM90-1280

TM90-1260

TM180-1424

TM180-1288

Desaturation

Heating

current

current

0 1 2 3 4Water content (%)

100

101

102

103

104

105

106

Am

plit

ude (

m)

Frequency: 0.18 HzTM90-1280

TM90-1260

TM180-1424

TM180-1288

Desaturation

Heating

current

current

Figure 5

(a) (b)

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10-1

100

101

102

103

104

105

Frequency (Hz)

101

102

103

104

105

Am

plit

ude (

m)

w=0.11%

w=0.4%

w=1.14%

w=2.07%

w=2.27%w=2.74%

w=3.13%

TM 90-1280Heating phase:

Desaturation phase:

Figure 6

0 1 2 3 4Water content (%)

100

101

102

103

104

PF

E (

%)

TM90-1280

TM90-1260

TM180-1424

TM180-1288

Desaturation

Heating

Figure 7

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0 1 2 3 4

Water content (%)

101

102

103

104

-Ph

ase

(m

rad

)Frequency: 12 kHz

TM90-1280

TM90-1260

TM180-1424

TM180-1288

Desaturation

Heating

0 1 2 3 4

Water content (%)

10-1

100

101

102

103

-Ph

ase

(m

rad

)

Frequency: 0.18 HzTM90-1280

TM90-1260

TM180-1424

TM180-1288

Desaturation

Heating

Figure 8

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10 15 20 25 30 35

Real part ( m)

0

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inary

part

(m

)

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CPA model

Cole-Davidson model

Figure 10

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0.183 Hz

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Figure 11

0 0.2 0.4 0.6 0.8 1 1.2

Real part of normalized Resistivity ( m)

0

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Figure 12

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Compaction of quartz sands by pressure solution

using a Cole-Cole distribution of relaxation times

A. Revil,1 P. Leroy,1 A. Ghorbani,2 N. Florsch,2 and A. R. Niemeijer3

Received 7 November 2005; revised 6 May 2006; accepted 5 June 2006; published 19 September 2006.

[1] Stressed water-infiltrated silica rocks may deform by pervasive pressure solutiontransfer (PPST), which involves dissolution of the grain-to-grain contacts, transport bydiffusion of the solute, and precipitation on the free surfaces of the grains. A fundamentalquestion regarding this process is how to model rheological behavior at stresses andtemperatures typical of the crust of the Earth. A Voigt-type poroviscoplastic model ismodified by using a Cole-Cole distribution of relaxation times rather than a Diracdistribution used previously. The motivation of this choice is to account forthe distribution of the grain size in the compaction of the porous aggregate assuming thatthis distribution obeys approximately a log normal distribution. This grain size distributiondepends upon the initial grain size distribution and cataclasis in the early stage ofcompaction. We compared this modified viscoplastic model with the full set ofexperimental data obtained in various conditions of mean grain size, effective stress, andtemperature by Niemeijer et al. (2002). These data provide tests of all aspects of themodel, which can be considered to have no free parameters. We show the experiments ofNiemeijer et al. (2002) on PPST are primarily diffusion-limited. The grain sizedistributions observed for three samples imply that the distribution of the relaxation timecovers 5 orders of magnitude in grain size.

Citation: Revil, A., P. Leroy, A. Ghorbani, N. Florsch, and A. R. Niemeijer (2006), Compaction of quartz sands by pressure solution

using a Cole-Cole distribution of relaxation times, J. Geophys. Res., 111, B09205, doi:10.1029/2005JB004151.

1. Introduction

[2] Pervasive pressure solution transfer (PPST) describesthe irreversible compactional process of mass transfer inrocks in response to stress and temperature fluctuations[e.g., Rutter, 1976, 1983; Niemeijer and Spiers, 2002;Skvortsova, 2004, and references therein]. Other mechanismof deformation are possible like those associated with micro-cracking [Karner et al., 2003]. PPST is associated with stressconcentration at grain-to-grain contacts increasing solubilityof the solid in the pore fluid, diffusion of the solute alonggrain-to-grain contacts, and precipitation on free faces of thegrains. The understanding of PPST can lead to the under-standing of locking/unlocking processes that affect granulargouge of active faults during the tectonic cycle (see recentpapers by Montesi [2004] and Yasuhara et al. [2005]) andcompaction of quartz sands in sedimentary basins [e.g.,Wahab, 1998]. In addition, PPST could explain soft creeprheology observed in the brittle-ductile transition zone of thecrust and within the seismogenic crust itself [Ivins, 1996].

[3] For quartz sands, several research scientists havemodeled pressure solution using a Newtonian viscous law[e.g., Rutter, 1976, 1983; Dewers and Hajash, 1995;Renard et al., 1997; Yang, 2000; He et al., 2002, 2003].In contrast, Stephenson et al. [1992] described the occur-rence of PPST of quartz sands in sedimentary basins, overlong periods of time, as being a purely plastic compaction.Revil [1999] proposed a unified model, which takes theform of a poroviscoplastic (Voigt-type) linear model with asingle relaxation time associated with the mean grain size ofthe porous medium (Figure 1). The microscopic reasons forthis behavior were explored by Revil [2001], who proposedthe existence of a stress threshold at the grain-to-grain contactbelow which PPST stops. Additional evidences in favor ofthis model were recently presented by Yasuhara et al. [2003,2004, 2005] and Alcantar et al. [2003]. Implications of thismodel for travelling solitary waves were explored by Yang[2002]. However, there is the need to test further the validityof the model for a wide range of mean grain sizes, temper-ature, and effective stresses and to incorporate in this model awider grain size distribution than just using a single value forthe grain size.[4] In section 2, the model of Revil [1999] is modified to

account for the distribution of grain size in the rheologicalmodel. To reach this goal, we use a Cole-Cole distribution ofrelaxation times (rather than a single value) in the viscoplasticresponse of the porous aggregate. This is equivalent toassuming that the grain size distribution obeys a log normaldistribution. The model of Revil [1999] is also modified to

JOURNAL OF GEOPHYSICAL RESEARCH, VOL. 111, B09205, doi:10.1029/2005JB004151, 2006ClickHere

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1Department of Hydrogeophysics and Porous Media, CNRS-CEREGE,University Paul Cezanne-Aix-Marseille III, Aix-en-Provence, France.

2Department of Applied Geophysics, University Paris VI, Paris, France.3High Pressure and Temperature Laboratory, Faculty of Geosciences,

Utrecht University, Utrecht, Netherlands.

Copyright 2006 by the American Geophysical Union.0148-0227/06/2005JB004151$09.00

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account for the nonlinear behavior of the deformation/effective stress constitutive law observed at high effectivestresses (section 3). Despite the fact that this modificationchanges the results little at effective stress conditions pre-vailing in the upper crust of the Earth, it seems to us importantto extend our model to a wide range of T-P conditions. Insection 4, a nonlinear optimization scheme based on theSimplex algorithm is used to compare the compactionalmodel to all the experimental data of Niemeijer et al.[2002]. Niemeijer et al. [2002] presented a unique series ofexperimental data in which they investigated the influence oftemperature (in the range 400–600C), effective stress (in therange 50–150 MPa), and mean grain size (10–86 m) uponthe compactional response of several quartz aggregates. Inaddition, the grain size distributions resulting from thecompaction process and cataclasis was measured byNiemeijer et al. [2002] for three samples, spanning over2 orders of magnitude in grain size. Consequently, thesedata offer a unique opportunity to test our compaction model.[5] Five predictions made by our model are tested for the

first time in this paper: (1) The plastic limit of the compac-tional response of the porous aggregate is independent ofthe mean grain size of the aggregate. (2) The temperaturedependence of the (long-term or plastic) compaction coef-ficient can be determined using an Arrhenius law. (3) Themean relaxation time of the viscoplastic model can be

described (within a factor 2) using the mean grain diameterof the aggregate and temperature. (4) The relaxation timedistribution (RTD) can be directly related to the particle sizedistribution (PSD) assuming a log normal distribution for thelatter; the model should be flexible enough to incorporateother PSDs. (5) The same compactional model can be used toexplain the full range of data obtained by Niemeijer et al.[2002] including the short-term viscous behavior and thelong-term plastic limit.

2. Theoretical Background

2.1. Debye Distribution of Relaxation Times

[6] We make the following assumptions: (1) the rock isan isotropic granular material, (2) the mineral of the granularaggregate is silica, and (3) in this section the grain size

Figure 1. Sketch of the compactional model. (a) The deformation of a representative elementary volumeof quartz sand follows a linear poroviscoplastic (Voigt-type) rheological behavior. The springs in parallelwith the dashpot represent the plastic (thermostatic) equilibrium state, whereas the dashpots represent thekinetics of PPST at the grain-to-grain contacts (the dashpots ‘‘p’’ and ‘‘d’’ correspond to dissolution/precipitation chemistry and diffusion-limited processes, respectively) (modified from Revil [2001]). Anadditional spring models the poroelastic response of the medium. (b) Analogy between a Voigt-typeviscoplastic model (a dashpot in parallel with an anelastic spring) and an electrical circuit in which a resistor(R is the resistance) is in parallel with a capacitor (C is the capacitance). Such an electrical model isclassically used to model the induced polarization response of water-saturated porous rocks.

Table 1. Temperature Dependence of Model Parametersa

Parameter Temperature Dependence = 0 exp(E/RT)

Solubility C0 = 67.6 kg m3 (1) EC = 21.7 kJ mol1 (1)Diffusivity D0 = 5.2 108 m2 s1 (2) ED = 13.5 kJ mol1 (2)Rate constant k+

0 = 31.3 mol m2 s1 (3) Ek = 71.3 kJ mol1 (3)Compressibility 0 = 2.6 108 Pa1 (4) E = 17 kJ mol1(4)

aNotes: 1, Iler [1979]; 2, Revil [2001]; note for comparison, Dewers andOrtoleva [1990] used D0 1 108 m2 s1 and ED = 40 kJ mol1 whileNakashima [1995] used ED = 15 kJ mol1; 3, Dove and Crerar [1990]; 4this work.

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distribution obeys a delta (Dirac) distribution with d0 themean grain size. Under these assumptions and neglectingmechanical deformation (grain rearrangement [e.g., Revil etal., 2002]), the compactional response of the porous aggre-gate is described by the following linear constitutive law[Revil, 1999]:

~ tð Þ ¼ tð Þ deff tð Þ

dtþ eff tð Þ

d tð Þ

dt; ð1Þ

~ tð Þ 0 tð Þð Þ=0; ð2Þ

tð Þ 1 exp t=0ð Þ½ ; ð3Þ

where circled cross stands for the Stieltjes convolutionproduct. In equations (1)–(3), t is time, (t) is the time-dependent compressibility of the porous aggregate, is itslong-term plastic compressibility (compaction coefficient),0 is the relaxation time, eff = p is the effective stress, is the confining pressure, p the pore fluid pressure, (t) isporosity at time t, and 0 is the initial porosity at thebeginning of the PPST process. The origin of time coincideswith the instant at which the material, in a relaxed referencestate, is subjected to the application of effective stress. The

porosity 0 is the porosity following the application of thestress. So that the initial poroelastic compaction representsthe starting reference state; initial poroelastic compaction isinvestigated in Appendix A. This elastic compaction processfollows instantaneously the stress variations and is reversible.[7] The rock behavior is modeled to have memory of the

highest effective stress experienced by the grain-to-graincontact during its history because of the increase of the grain-to-grain contiguity associated with the compaction. Theprevious compactional response holds as long as

deff =dt 0: ð4Þ

When the effective stress decreases, the deformationresponse follows essentially a poroelastic behavior corre-sponding to the relaxation of the elastic energy stored in thesample.[8] The relaxation time in equation (3) is given by

(Figure 1a),

0 ¼ =Q; ð5Þ

Q1 ¼ Q1d þQ1

p ; ð6Þ

Qd ¼32W

kbT

C!D

gd30; ð7Þ

Qp ¼3W2

kbTN

d0; ð8Þ

where T is the temperature (in K), C (in kg m3) is thesolubility of the grain surface in the pore water solution inequilibrium with quartz at fluid pressure and temperature, !is the effective thickness of the diffusion pathways at thegrain-to-grain contacts (2 nm, see discussions by Revil[2001]), D (in m2 s1) is the diffusivity of silica at the grain-to-grain contacts, d0 (in m) is the grain diameter, W is themolecular volume of silica (3.77 1029 m3), k+ is thedissolution rate constant, kb is the Boltzmann constant(1.381 1023 J K1), g is the density of the grains, and Nis Avogadro’s number (6.02 1023 mol1). The numericalconstants entering equations (7) and (8) and the temperaturedependence of the various parameters involved in theseequations are reported in Table 1.[9] Revil [2001] showed that diffusion of the solute at the

grain-to-grain contacts is one or 2 orders of magnitudesmaller than that in the bulk pore water. This was recentlyconfirmed by laboratory experiments [e.g., Alcantar et al.,2003; Yasuhara et al., 2003, 2004]. In low-porosity shalesand in compacted bentonites (both having small pore sizes),Revil et al. [2005] and Leroy et al. [2006] reached similarconclusions based on modeling of coupling phenomena thataffects diffusion of ionic species in charged media.[10] The model of Revil [1999] corresponds to a Voigt-

type linear viscoplastic model represented by a dashpot inparallel with an anelastic spring. From the perspective of thedifferential equation governing the system, the behavior isanalogous to an electrical circuit formed by a resistor in

Figure 2. Distribution of relaxation times P(s) where s ln( /0) for various values of the Cole-Cole exponent c. Notethat smaller values of the exponent corresponds to broaderdistributions of relaxation times. The case c = 1 yields a Diracdistribution. The case 0.5 c 1 is very similar to aGaussian distribution. For c < 0.5, the Cole-Cole distributionhas a longer tail than the Gaussian distribution.

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parallel with a capacitor (Figure 1b). In this case, therelaxation time is given by a Dirac (delta) distribution andtakes the discrete value 0. In the study of the inducedpolarization of porous materials, this is known as a Debyerelaxation or distribution.

2.2. Cole-Cole Distribution of the Relaxation Times

[11] When the grain size distribution cannot be describedby a unique value, the relaxation time distribution (RTD)exhibited by the compactional response of a porous aggregatecannot be described by a single value of the relaxation time,hence by a Dirac distribution. If the effective stress variationfollows a Heaviside (step) distribution, grain crushing asso-ciated with cataclasis in the first stage of deformation,increases the distribution of the grain size [e.g., Gratier etal., 1999]. This distribution needs to be accounted for, at leastin a simple fashion, in the compactional law. Indeed, becauserelaxation times entering the compaction law are directlyassociated with the grain size distribution (equations (5) to(8)), a wide distribution of grain sizes implies a widedistribution of relaxation times. The inclusion of a realistic

RTD is especially important if the process is diffusion-limitedbecause of the power law relationship relating the grain sizesand the relaxation times in that case (equations (5) and (7)).[12] In the study of the electrical properties of saturated

porous rocks, it is customary to represent broad distributionsof relaxation times in the induced polarization of saturatedrocks and soils with the so-called ‘‘Cole-Cole’’ distribution[see Cole and Cole, 1941; Taherian et al., 1990]. The Cole-Cole distribution is characterized by a single coefficient, c,that accounts for the broadness of the distribution of relax-ation times and therefore of the broadness of the distributionof the grain sizes [see Chelidze et al., 1977; Pelton et al.,1978; Chelidze and Gueguen, 1999; Kemna, 2000].[13] Under the assumption that the distribution of relax-

ation times is represented by a Cole-Cole distribution, thecompressibility of our rheological model becomes

tð Þ F t=0; cð Þ; ð9Þ

F t=0; cð Þ 1X

1

n¼0

1ð Þn t0

nc

G 1þ ncð Þ; ð10Þ

F t=0; cð Þ X

1

n¼1

1ð Þnþ1 t0

nc

G 1þ ncð Þ; ð11Þ

where G( ) is the gamma function defined by

G xð Þ ¼

Z

1

0

ux1eudu ð12Þ

(x > 0). Note that the series development involved inequation (11) converges very slowly for t/0 > 10 and c < 1;thus a significant number of terms is required for a goodconvergence of the series. In the case c = 1, we recover theDebye distribution

F t=0; 1ð Þ X

1

n¼1

1ð Þnþ1 t0

n

G 1þ nð Þ; ð13Þ

F t=0; 1ð Þ 1X

1

n¼0

1ð Þn t0

n

G 1þ nð Þ; ð14Þ

Ft

0; 1

1X

1

n¼0

t0

n

n!¼ 1 exp

t

0

; ð15Þ

as required for the internal consistency of the model. TheRTD is given with the probability [Cole and Cole, 1941]

P sð Þ ¼1

2

sin 1 cð Þ½

cosh csð Þ cos 1 cð Þ½ ; ð16Þ

Figure 3. Long-term compaction coefficient is deter-mined using the plastic equilibrium compactional responseof the aggregates and optimization of the model parameters.The solid circles correspond to the data from Niemeijer etal. [2002] (all runs). (a) The temperature dependence of thecompaction coefficient can be described using an Arrhenius’slaw. (b) The compaction coefficient does not depend on themean grain size. The thickness of the grey band representsthe uncertainty in the determination of the compactioncoefficient.

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where s ln( /0), describes the distribution of relaxationtimes and 0 describes the peak of relaxation times given insection 2.1. The peak of the RTD is associated with the peakd0 of the grain size distribution and c characterizes thebroadness of the distribution. The probability distributionP(s) has the property

Z

þ1

1

P sð Þds ¼ 1: ð17Þ

The Cole-Cole equation produces a very broad distribution ofrelaxation times when c is small (see Figure 2). For examplefor c = 0.25, 72 percent of the relaxation times are included inthe range 103 < /0 < 10

3. When c is in the range 0.5–1, theCole-Cole distribution is quite similar to a log normaldistribution. However, the Cole-Cole distribution has alonger tail than the log normal distribution when c is less than0.5. The parameter c introduced in our model is not just acurve fitting parameter. It corresponds directly to thestandard deviation of the logarithm of the grain sizedistribution assuming a log normal distribution. Accordingto the dependence between relaxation times and the grain size(equations (5), (7), and (8)), the RTD can be compareddirectly with the particle size distribution (PSD).[14] Some granular aggregates may exhibit RTDs that are

not described by the Cole-Cole distribution. In these cases,other types of distribution can be considered in our model.For example, the Cole-Davidson distribution [Davidson andCole, 1951] can account for nonsymmetrical PSD distribu-tions of sediments or fault gouge. Using the properties ofthe convolution product, any distribution can be consideredcorresponding to a given grain size distribution. However,the mathematics are likely to become complex, and we willtreat this elsewhere. In the present model, we show that thelog normal PSD is a good approximation and thereforejustifies the use of the Cole-Cole distribution.

3. Deviation From the Linear Model

[15] We now adapt the model of Revil [1999] to a widerange of effective stresses. At high effective stresses (typi-cally 100 MPa), the experimental data by Niemeijer et al.[2002] show a clear departure from the linear model proposedin section 2. In the case of these experimental data, theeffective stress history is simply

eff tð Þ ¼ effH tð Þ; ð18Þ

where H (t) is the Heaviside or step function (H (t) = 0 fort < 0 and H (t) = 1 for t 0) and eff is the imposed(constant) effective stress. Under this situation, the convolu-tion integral in equation (1) yields the following linearcompactional response

tð Þ ¼ 0 1 tð ÞeffH tð Þ

ð19Þ

tð Þ ¼ 0 1 F t=0; cð ÞeffH tð Þ

: ð20Þ

Figure 4. Comparison of the model predictions andlaboratory experiments for the long-term compactionalresponse 1/0 of porous aggregates. (a) Test of the linearrelationship is shown. Note the discrepancy between the dataand the model at high effective stresses. (b) Test of theexponential relationship is shown. The experiments cover abroad range of temperatures (400 to 700C) and effectivestresses (50 to 344 MPa) (solid circles, Niemeijer et al.[2002]; solid squares, Lockner and Evans [1995]). The finalporosity is independent of the mean grain size. Indeed, thesamples cover a broad mean grain size spectrum (from 5 to85 m). The gray bands represent uncertainty in determina-tion of the porosity ratio.

Table 2. Conditions of the Experiments of Niemeijer et al. [2002]a

Run T, C d, m eff, MPa ib f

c

Cpf3 500 47.1 100 0.2731 0.1271Cpf4 500 42.9 150 0.2350 0.1051Cpf5 500 40.5 50 0.2612 0.1660Cpf6 400 40.9 100 0.2514 0.1536Cpf7 600 43.2 100 0.3138 0.0970Cpf8 500 11.7 100 0.3108 0.1465Cpf9 500 85.9 100 0.2451 0.1032

aThese experiments cover a wide range of effective stresses, temper-atures, and mean grain size.

bPorosity at the beginning of the compaction process.cPorosity at the end of the compaction process.

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We show now that the previous equations can be modifiedto account for the observed nonlinear behavior of thecompactional response at high effective stresses.

3.1. Long-Term Plastic Limit

[16] The long-term limit of the compactional response ofthe porous aggregate corresponds to timescales for whichthe duration of the experiment is much larger than the peakof the distribution of the relaxation times. When t 0, thecompactional response reaches a linear ‘‘plastic’’ limit[Stephenson et al., 1992]

1=0 ¼ 1 eff : ð21Þ

The term ‘‘plastic’’ means that the compactional response isirreversible and that time does not appear explicitly in theconstitutive rheological law. Equation (21) is valid under theassumption that eff 1 [Revil, 2001] and a linearization ofthe compaction law can be performed. However, experimentsperformed at high effective stresses show unambiguously that

there is a deviation from linearity [see, e.g., Niemeijer et al.,2002, Figure 2b]. We propose to correct this nonlinearity byreplacing equation (21) with the plastic limit

1 ¼ 0 exp eff

; ð22Þ

which admits equation (21) as a limit when eff 1, so forlow effective stress levels (100 MPa). Our choice of anexponential law is related to the exponential relationshipbetween the solubility and the effective stress at themicroscopic level.[17] The first prediction of our model (prediction 1) is

that the poroplastic limit is independent of the grain sizedistribution of the quartz sand. This prediction is in agree-ment with the experimental data of Niemeijer et al. [2002,Figure 2d]. Indeed for experiments performed with a widerange of mean grain sizes, in the range 12–86 m (not to bemisled with the grain size distribution of each sample), thecompactional response 1/0 was observed for the narrowrange 0.40–0.48. Figure 3b shows that the compactioncoefficient is independent on the mean grain size of theporous aggregates.[18] The dependence of the compaction coefficient on

temperature is determined using an Arrhenius’s law for (Table 1) (prediction 2). Note that is inversely proportionalto the critical stress c, which defines the limiting stressthat grain-to-grain contacts can support without creeping[Stephenson et al., 1992; Revil, 2001]. A similar behaviorcould exist for tectonic faults. We expect that the criticalstress sc is temperature-dependent. Revil [1999] used a lineardependence between this critical stress and the temperature.The dependence of the compaction coefficient on temper-ature can be also fitted with an Arrhenius law. This Arrhe-nius law is calibrated against the data of Niemeijer et al.[2002]. The final result is shown in Figure 3a and is reportedin Table 1.[19] A comparison between the long-term linear compac-

tion law (equation (21)) and the exponential law(equation (22)) (Figure 4) shows that the exponential lawprovides a better description of the experimental data in theplastic limit of compaction. As these experimental data covera broad range of temperatures (400 to 700C) and effectivestresses (50 to 344 MPa), the exponential model is likely tobe more appropriate than the linear model.

3.2. Short-Term Compaction

[20] As for the long-term limit of compaction, we have toaccount for the nonlinear behavior discussed above for the

Figure 5. (a) Compaction curve of a quartz aggregate inthe initial stage of deformation. Data are fromNiemeijer et al.[2002] (run Cpf8, effective pressure: 100 MPa, mean graindiameter: 12 m, effective stress 100 MPa, temperature500C, i = 0.311). (b) Comparison between the predictedporosity and the measured porosity is shown. (c) Comparisonbetween the measured grain size distribution and thatpredicted using the Cole-Cole distribution (plain line) isshown.

Table 3. Model Prediction of Experiments of Niemeijer et al.

[2002]

Run Qp,a Pa s1 Qd,

a Pa s1 Qd,a Pa s1

LimitedProcessb

0,c

hours

Cpf3 6.70 1014 1.20 1014 1.02 1014 DL 145Cpf4 7.36 1014 1.59 1014 1.31 1014 DL 113Cpf5 7.79 1014 1.89 1014 1.52 1014 DL 97Cpf6 17.0 1014 9.32 1015 6.02 1015 DL 174Cpf7 2.31 1013 2.58 1014 2.32 1014 DL 83Cpf8 2.70 1013 7.83 1013 2.01 1013 DPL 7.4Cpf9 3.67 1014 1.98 1015 1.88 1015 DL 788

aDetermined from equations (6), (7), and (8).bDL, diffusion limited; DPL, dissolution/precipitation kinetics limited.cDetermined from equation (5) and Table 1.

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full compactional response following the application of thestress. Indeed, very high values for the effective stresses wereused in the experiments described by Lockner and Evans[1995] and Niemeijer et al. [2002]. Therefore we replaceequation (19) by

tð Þ ¼ 0 exp tð Þeff

H tð Þ; ð23Þ

for t > 0. equation (23) admits equation (19) in the limiteff 1.

4. Comparison With Experimental Results

[21] We use all the experimental data by Niemeijer et al.[2002] to test the compaction model developed above.Seven experiments were reported by Niemeijer et al. [2002]at various conditions of temperature, mean grain size, andeffective pressure typical of the crust of the Earth. Theseconditions are reported in Table 2. Niemeijer et al. [2002]point out that an abrupt change in strain rate occurred, in allruns, after a few hours to 12 hours. They argue that thiscould be due to the fact that dissolved copper strongly hindersthe dissolution rate of quartz and infiltration of dissolvedcopper from the cell into the samples during these experi-ments may have slow down compaction. However, suchcontamination is difficult to explain because the flux ofwater is outward from the samples during their compac-tion. Diffusion is a too slow process at this timescale

Table 4. Results of Inversion for Experimental Data of Niemeijer

et al. [2002]a

Run 0 c , 108 Pa1

Cpf3 0.276 ± 0.002 0.35 ± 0.01 1.80 ± 0.02Cpf4 0.245 ± 0.002 0.31 ± 0.01 2.45 ± 0.01Cpf5 0.266 ± 0.002 0.34 ± 0.01 1.95 ± 0.03Cpf6 0.262 ± 0.002 0.28 ± 0.01 1.17 ± 0.03Cpf7 0.313 ± 0.002 0.31 ± 0.01 2.45 ± 0.13Cpf8 0.308 ± 0.004 0.29 ± 0.01 1.07 ± 0.04Cpf9 0.256 ± 0.002 0.30 ± 0.01 2.53 ± 0.04

aThe reported values are the mean and twice the standard deviation of thea posteriori distributions of the model parameters.

Figure 6. (a) Compaction curve of a quartz aggregate inthe initial stage of deformation. Data are fromNiemeijer et al.[2002] (run Cpf3, effective pressure 100 MPa, mean graindiameter 47 m, effective stress 100 MPa, temperature500C, i = 0.273). (b) Comparison between the predictedand measured porosities is shown. (c) Comparison betweenthe measured grain size distribution and that predicted usingthe Cole-Cole distribution (plain line) is shown.

Figure 7. (a) Compaction curve of a quartz aggregate inthe initial stage of deformation. Data are fromNiemeijer et al.[2002] (run Cpf9, effective pressure 100 MPa, mean graindiameter 86 m, effective stress 100 MPa, temperature500C, i = 0.24). (b) Comparison between the predicted andmeasured porosities is shown. (c) Comparison between themeasured grain size distribution and that predicted using theCole-Cole distribution (plain line) is shown.

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over the length of the sample to allow copper to infiltratethrough its pore network. As shown below, there is noneed of such an hypothesis to explain the shape of thecompaction curves.[22] There are also some controversies regarding the

relative roles of pressure solution versus cracking at grain-to-grain contacts. Cataclastic compaction by cracking that isfluid-assisted through reaction at the crack tip (and thereforethermally activated) can also be an important process ofcompaction, and the samples of Niemeijer et al. [2002] showabundant evidence of cracking. However, the high temper-atures of the Niemeijer et al. [2002] experiments would tendto favor pressure solution as the dominant mechanism ofdeformation.

[23] For t > 0, the nonlinear compactional law is writtenexplicitly as

tð Þ ¼ 0 exp effX

1

n¼1

1ð Þnþ1 t0

nc

G 1þ ncð Þ

2

4

3

5: ð24Þ

[24] We first compare the prediction of this equation withthe experimental data in the early stage of compaction (seeFigures 5 to 8) using the fitting algorithm described inAppendix B. In Figure 9, we plot the mean relaxation times0 determined by fitting equation (24) to the experimentaldata as a function of the relaxation times derived indepen-dently, in Table 3, using equations (6), (7), and (8). There is

Figure 8. Compaction curves of quartz aggregates in the initial stage of deformation. Data are fromNiemeijer et al. [2002]. The parameters given are fitted parameters, but their values are very close toindependent evaluations from the equations developed in section 2.

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good agreement between the two estimates, so it followsthat prediction 3 of the model is fine (the mean relaxationtime of the viscoplastic model can be described (within afactor 2) using the mean grain diameter of the aggregate andtemperature). Therefore, to diminish the number of fittingparameters when we consider all the experimental data, weuse the value of the relaxation time 0 directly inferred fromequations (6), (7), and (8).[25] From the considerations given above, the parameters

to invert are 0, , c. We use the inversion algorithmdescribed in Appendix B. The results of the inversion, forthe full set of the experimental data, are reported in Table 4.The fitted porosity 0 is very close to the initial porosity.This is expected from the small contribution of the poroe-lastic contribution (see demonstration in Appendix A). Thecompaction coefficient increases with temperature accord-ing to the Arrhenius law (Figure 3a) and the range of valuesof the compaction coefficient is consistent with that reportedby Revil [2001]. The value of c implies a broad relaxationtime distribution in agreement with the observed PSD(Figures 5, 6, 7, and 8) and the fact that the process isdiffusion-limited. Indeed, as shown in Table 3, the kineticsof the compaction experiments are limited by the diffusionof the solute species at the grain-to-grain contacts. Thisimplies that the relaxation time is an function of the grainsize with a power law exponent equal to three, in agreementwith available data (see Figures 5c, 6c, and 7c). Soprediction 4 of the model, stated at the end of section 1,is also checked.[26] All the parameters involved in our compaction model

can be obtained independently. It follows that the only

factor that must be adjusted in our model is the Cole-Coleexponent. From the experiments made by Niemeijer et al.[2002], the Cole-Cole exponent falls in a narrow rangec = 0.30 ± 0.05. It follows that this range of values isrecommended to model pervasive pressure solution transferin such materials. Additional experiments would be useful totest whether the parameter value c = 0.30 is universal. If so,our model has no free parameters. The compaction modelwith c = 0.30 and experimental data are compared in Figure 9and Figure 10. The agreement between the model and theexperimental data provides a test of prediction 5: the samecompactional model can be used to explain the full range ofdata obtained by Niemeijer et al. [2002] including the short-term viscous behavior and the long-term plastic limit.[27] If the grain size distribution evolves during compac-

tion, this implies that the value of c (that reflects the standarddeviation of the lognormal distribution of the PSD) changesduring the compaction. For example, if the grain size distri-bution appears more restricted at the end of the experimentsthan at the start of a run, this implies that the value of cincreases during the experiment. Inversion for c, at differenttime steps, during compaction may be used to monitor theevolution of particle size distribution with time. This could beimportant for permeability modeling, for example, duringfault zone healing (T. Dewers, personal communication,2005).

5. Concluding Statements

[28] The model of Revil [1999] is modified using a Cole-Cole distribution of relaxation times and nonlinear com-pactional law at high effective stresses. The Cole-Cole

Figure 9. Comparison between the mean time 0 constantobtained by fitting the data to equation (24) (values reportedin Figures 5 to 8) and the time constant determinedindependently from equations (5) to (8) and the values ofparameters in the last column of Table 3. Cpfi corresponds tothe experimental run ‘‘i’’. The grey band represents theuncertainty in determination of the mean relaxation time.

Figure 10. Test of the model for the effective stress. Thecompaction model is compared to compaction curves of threequartz aggregates, at the same temperature, but at differenteffective stresses (c = 0.30 and all the other parameters aredetermined from the equations developed in themain text andTable 1). Experimental data are from Niemeijer et al. [2002].

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distribution is characterized by a single exponent c, whichaccounts for the distribution of the relaxation times. The casec = 1 corresponds to a Dirac distribution, which is in turnassociated with a very sharp distribution of grain size (e.g., aGaussian distribution with a very small variance). The use ofa Cole-Cole response is intended to account for large grainsize distributions in the compactional response of the porousaggregates. This modified model is compared to the exper-imental data obtained byNiemeijer et al. [2002] for which thegrain size distributions cover more than 2 orders of magni-tude, resulting in part from cataclasis in the early stage ofdeformation. We find a good agreement between the predic-tion of the model and the experimental data with c = 0.30 ±0.05. Because the kinetics of compaction are limited bydiffusion (see Table 3), we expect that the RTD covers 5–6 orders of magnitude. This is in agreement with theprevious value for the Cole-Cole exponent. Broad distribu-tions of grain size likely exist during natural compaction anddeformation of fault gouge.[29] This new model has important implications for the

dynamics of faults, the compactional response of sandstonesin sedimentary basins, and subsidence related to changes ofthe effective stress in clastic oil/gas reservoirs. The modelyields different predictions for the compactional response ofporous aggregates from those using other rheologies (e.g.,viscous or poroelastic). This model has also some applica-tions to the study of solitary waves in the crust of the Earth[see Revil and Cathles, 2002; Revil et al., 2003].

Appendix A: Poroelastic Contribution

[30] The total porosity change of the porous aggregate iswritten as

@ tð Þ

@t¼

@

@t

e

þ@

@t

i

; ðA1Þ

where the first term of the right-hand side of equation (A1)(subscript e) corresponds to the poroelastic contribution andthe second term of the right-hand side of equation (A1)(subscript i) corresponds to the (irreversible) compactionalresponse associated with pressure solution. In Biot’s theory,the poroelastic contribution to deformation is given by

@ tð Þ

@t

e

¼ e@

@t

@p

@t

; ðA2Þ

where is the porosity, is the confining pressure, and p isthe pore fluid pressure. The elastic porosity compressibilitye and the porosity effective stress coefficient are definedby

e ¼1

B

1

K

1

Ku

KðA3Þ

¼=Kf þ 1=Bð Þ 1=K 1=Kuð Þ=B

=K 1=K 1=Kuð Þ=B; ðA4Þ

where B is the Skempton’s coefficient, K is the drained bulkmodulus, Ku is the undrained bulk modulus, and Kf is the

bulk modulus of the pore water. A simple analysis of theporoelastic compactional response indicates that it is muchsmaller than the PPST response in the experiments byNiemeijer et al. [2002]. Typically, (/)e < 5%.

Appendix B: Fitting Procedure

[31] Equation (24) can be expressed as a nonlinearfunctional relationship of the form d = G(m) between thevector of model parameters m and the vector of porositydata d:

d ¼ 1; 2; . . . ; 3½ T ðB1Þ

m ¼ 0; ; c½ T ; ðB2Þ

where T signifies transpose. We use an a priori densityprobability corresponding to the null information in therange of possible values of the model parameters, which are0 2 [0.20; 0.35], b 2 [0.5 108/Pa; 3.0 108/Pa], andc 2 [0; 1]. The Simplex algorithm [Caceci and Cacheris,1984] is used to minimize the least squares objectivefunction

minR ¼k G mð Þ d0 k2; ðB3Þ

where kvk = (vTv)1/2 denotes the Euclidian (L2) norm and dois the vector of the observed porosity data.[32] We use an a priori model chosen randomly in the a

priori set of values of the model parameters given above.Then, we determine the mean and the standard deviation ofthe optimized model parameters resulting from the use ofthe optimization process. Five hundred terms were consid-ered in the series development involved in equation (24).The results are reported in Table 4.

[33] Acknowledgments. A.R. is grateful to L. M. Cathles for fruitfuldiscussions when he was at Cornell University and the American RockMechanic Association (ARMA) for the 2004 Rock Mechanics ResearchAward he received and which has stimulated the present work. ANDRA isthanked for a grant given to P. Leroy during his Ph.D. thesis. This paperis the GDR-FORPRO Contribution 2005/11A.D and is also a contributionfrom the project POLARIS (ANR-ECCO-PNRH). D. Coelho, S. Altmann,and J. Lancelot are thanked for their supports. We thank J. Weertman,Andreas Kronenberg, E. H. Rutter, T. Dewers, and two anonymous refereesfor their constructive comments regarding this work.

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A. Ghorbani and N. Florsch, University Paris VI, UMR 7619 ‘‘Sisyphe’’Universite Pierre et Marie Curie, Paris 6, Tour 56, 4 place Jussieu, F-75252Paris Cedex 05, France.P. Leroy and A. Revil, CNRS-CEREGE, BP 80, F-13545 Aix-

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General conclusion and perspectives

This thesis has been dealt with the evaluation and applications of SIP method in

environmental exploration is summarized in five papers. Two papers are presented in the

context of the inversion inference and inversion methods. The results of these papers are

following:

Bayesian approach was developed to invert of the Cole-Cole model parameters in the

time or in the frequency domains. The Bayesian approach consists in propagating the

information provided by the measurements through the model, and to combine this

information with an a priori knowledge of the data.

We have shown that the Bayesian approach provides a better analysis of the uncertainty

associated with the parameters of the Cole-Cole model by comparison with more

conventional methods based on the minimization of a cost function using the least-square

criteria. The Bayesian approach allows delineating “equivalent domains” in the space of the

model parameters accounting for the uncertainty in the measurements.

The Bayesian procedure results demonstrated that the classical time domain approach cannot

lead to a proper estimate of the Cole-Cole parameters. Morover, the frequency domain

induced polarization signals that use the harmonics of square current signals in a low

frequency range cannot lead to estimate the Cole-Cole parameters.

On the opposite, the Cole-Cole parameters can be more correctly inverted in the frequency

domain. These results are also valid for other models describing the SIP response like the

Cole-Davidson or power law models.

We developed the 1D inversion of IP and EM coupling integral according to forward

modeling code taken from Ingeman-Nielsen and Baumgartner (2006). We used the general

Homotopy method, as path tracking is based on a set of predictor–corrector steps. The

corrector steps are Gauss–Newton or Quasi Newton sequence of iterations. The inversion

results show the recovered parameters agree well with the true values.

Two other papers are presented in the context of the experimental applications of SIP

method. The results of these papers that are following:

Spectral induced polarization is used to monitoring of the water infiltration in a clay loamy

soil. Both in situ and soil column experiments were based on the coupled acquisition of

tensiometer data and SIP spectra (1.46 Hz to 12 kHz) during a water infiltration achieved by a

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artificial constant rainfall rate of about 15 mm/hr. This approach confirmed the existence of

significant phase drops in the high-frequency domain (typically greater that 1 kHz) during the

first infiltration cycles. The crossed interpretation of tensiometer data and SIP data has shown

that these phase drops were correlated with the water filling of pores whose equivalent

diameter were estimated in the range of [30-85 m]. This class of diameters correspond to the

transmission or structural pores.

These phase drops were qualitatively and quantitatively interpreted as a Maxwell-Wagner

effect: during the water infiltration, the decrease of the polarization amplitude is due to a

release of charge carriers initially blocked in the microporosity, leading macroscopically to a

decrease of the bulk soil polarizability.

Consequently, the experimental and theoretical results of this study suggest strongly that the

SIP method would be able to control in the field the water filling the structural pores.

Spectral induced polarization was used to monitor the water content and the thermally-

induced microcracks for four nearly water-saturated argillite samples of test site. The SIP

measurements (0.1 Hz to 12 kHz) recorded by a four-electrodes device, during two following

desiccation path: (a) a desaturation phase under ambient air and then (b) a heating phase

corresponding to four temperature levels (70 °C, 80 °C, 90 °C, and 105 °C).

The amplitude of the complex resistivity was extremely sensitive to water content change. At

the end of the isotherm desaturation phase, it has been multiplied by a factor of 3 to 5. During

the heating phase, the resistivity increased by more than two orders of magnitude compared to

the initial state. The percentage of Frequency Effect shows a low sensitivity to water content

changes during the desaturation stage while it increased by two orders of magnitude during

the heating phase. This result confirms that low-frequency spectral signature is extremely

sensitive to textural changes (i.e., thermal-induced microcracking in this case) that occurred

during heating. Moreover, the complex resistivity of the samples shows a strong anisotropy.

The best models to invert the dielectric spectra is the Cole-Cole model and the general Cole-

Cole model for the desaturation phase and the heating phase, respectively.

However, the data show that the development of the anisotropy can induced different spectral

signatures and polarization processes.

This work strongly suggests further experimental and theoretical investigations in three

directions.

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1 It is important to confirm in others sites that SIP method is able to provide

structural geometrical properties (types of pores and induced-microcracks

etc.).

2 Until now the application of the results of small-scale laboratory

experiments to large-scale field investigations has been very problematical,

especially in environmental geophysics. We have to develop relevant

conceptual tools to achieve the upscaling of the SIP parameters at different

scales.

3 The need to expand the frequency range towards both lower and higher

frequencies is evident and a one-decade increase of up to 104 Hz seems to

be realistic. Until now, the limitations are usually due to inductive

coupling. Electronic improvements have to be pursuing to enhance the

development of new applications in environmental geophysics.

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