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Proceedings of the Institution of Civil Engineers
Geotechnical Engineering 166 August 2013 Issue GE4
Pages 408–414 http://dx.doi.org/10.1680/geng.12.00010
Paper 1200010
Received 01/02/2012 Accepted 18/10/2012
Published online 22/02/2013
Keywords: foundations/piles & piling
ICE Publishing: All rights reserved
Geotechnical EngineeringVolume 166 Issue GE4
Chemical interactions at the concrete/clayinterface due to thaumasite form of sulfateattackBrueckner, Williamson and Clark
Chemical interactions at theconcrete/clay interface due tothaumasite form of sulfate attackRene Brueckner Dipl-Ing, PhD, CEng, MICoorMaterials/Corrosion Engineer, Mott MacDonald, Altrincham, UK
Sarah J. Williamson BEng(Hons), PhD, CEng, MIStructEStructural Engineering Leader, Laing O’Rourke, Dartford, UK
Les A. Clark OBE, FREng, BEng, PhD, CEng, FIStructE, FICEEmeritus Professor of Structural Engineering, The University ofBirmingham, Birmingham, UK
The stability of structures is determined by physical interactions between the foundations and the surrounding soil.
Concrete foundations are also subject to chemical interactions at the concrete/clay interface, which can result in
changes in the properties of the adjacent soil. The occurrence of the thaumasite form of sulfate attack particularly
affects the skin friction between the concrete and the ground. In this investigation of the chemical interactions at the
concrete/clay interface it was found that although an increase in moisture content and pH was confirmed, and this
moisture and pH gradient was also observed within the thaumasite layer, no further effects on the adjacent clay due
to thaumasite form of sulfate attack were found.
1. IntroductionBuried concrete foundations need to transfer the load of the
superstructure to the underlying soil formation without over-
stressing the latter (Cernica, 1995). Beside this, the performance
of other structures such as retaining walls depends on interfacial
interactions that are determined by both physical and chemical
effects. In the event of thaumasite sulfate attack (TSA) of buried
concrete changes in skin friction occur, as discussed by Brueck-
ner (2008) and Brueckner et al. (2012). The effect of TSA on
skin friction is generally positive, and therefore it was concluded
that substructures built without consideration of the effects of
TSA should be stable. TSA targets the calcium silicate hydrates
(C-S-H), which are the main binding agent in all Portland-
cement-based binders. Whereas the consumption of calcium
aluminate hydrates (C-A-H) during conventional sulfate attack
causes expansion and, ultimately, cracking of the cement matrix,
TSA leads to a transformation of the cement matrix into an
uncohesive mass from the surface inwards.
Beside the physical interactions, which are mainly responsible for
the stability, there are also chemical interactions between soil and
concrete piles/foundations that occur at the interface, or reach
within the clay. The presence of calcium and hydroxyl ions in the
pore water of the soil due to leaching from the cement paste
causes a sequence of reactions that vary with soil composition,
mineralogy and pore water chemistry, and according to Webster
and Sheary (1962) result in the following changes of the soil
j reduction of the plasticity index
j reduction of volume change
j flocculation of clay particles to make soils more friable
j increase in optimum moisture content, allowing compaction
under wetter conditions (soils dry out more rapidly)
j some increase in strength and stability.
Furthermore, the presence of hydroxyl ions (OH�) increases the
pH of the soil, which favours a solidification process as a result
of pozzolanic reactions in which, according to Sherwood (1993),
dissolution of silicon and aluminium from the clay takes place.
The dissolved components react with the calcium ions present in
the pore water and form C-S-H and C-A-H. According to El-
Rawi and Awad (1981), these reactions result in a significant
long-term increase in shear strength, and may often be combined
with a reduction of permeability. This feature has made the use
of lime and cement successful in the improvement of clay
properties, such as stabilisation.
Milititsky et al. (1982) showed, in their investigations on soil–
structure interactions, an increase in moisture content of the clay
of up to 4% after 7 days. However, the moisture content increase
falls rapidly away from the interface, as observed by Milititsky et
al. (1982), Chuang and Reese (1969), O’Neill and Reese (1970)
and Yong (1979). Lee (2001) investigated the interaction over a
period of up to 10 months, and observed that the increase in
moisture content decreases with time. The same trend was ob-
served for pH, which reached the natural soil value at a distance of
approximately 25 mm from the interface. This was similar to the
distance where the moisture increase was reduced to zero. The
influence of calcium ions was observed in increased concentrations
in the surrounding clay up to a distance of 75 mm over a period of
10 months, and this was reflected in the plasticity of the clay.
Hill et al. (2003) have started measurements on changes in pH
and chemical composition of the clay surrounding a pile which is
affected by sulfate attack; however, final data have not yet been
published.
408
After the TSA-affected bridge foundations along the M5 motor-
way in Gloucestershire were discovered in 1998, a part of the
subsequent comprehensive investigation included the effects of
TSA on the interface interactions, which were discussed by Slater
et al. (2003). Significant relationships between chemical, miner-
alogical or physical soil parameters and distance from the
concrete or degree of thaumasite attack were not found. However,
several trends were identified. Those relating to pure soil–
structure interactions were
j increase of moisture content towards the concrete
j increase of pH value towards the concrete
j increase of calcium concentration, derived from the leaching
of the calcium hydroxide from the concrete pore water
towards the concrete.
On the other hand, trends were observed in the clay adjacent to
the structure, which related to factors and features of the
thaumasite form of sulfate attack, as follows.
j Water-soluble magnesium decreased closer to the concrete,
and had an inverse relationship with pH.
j Pyrite and indirect sulfide concentration decreased with
increasing attack – that is, most thaumasite attack occurred
where there was most pyrite oxidation.
j Sulfates and total sulfur increased with increasing attack.
j Gypsum values were highest where there was partial attack,
and were depleted where there was full attack.
j The pH value and water-soluble magnesium increased and
decreased respectively with increasing attack.
The trends developed in relation to the availability of the
transport medium: that is, they are dependent on the groundwater
level. No attack was found above the maximum water level, and
full attack was encountered below the minimum water level that
corresponded to permanently wet conditions.
2. Methodology
2.1 General
The chemical interactions at the concrete/clay interface were
determined alongside the investigation of the effects of TSA on
skin friction at the concrete/soil interface reported by Brueckner
et al. (2012) using the same specimens.
2.2 Specimens
The investigation was carried out on specimens simulating a
concrete pile/soil interface at three different depths: 0.5 m, 2.0 m
and 3.5 m. The depth of clay on top of the concrete was 100 mm,
on which a reservoir of a 1.8% sulfate solution was maintained to
accelerate the thaumasite formation at the interface.
Two types of clay were used: a sulfate-containing illitic Lower
Lias Clay (LLC) and an inert kaolinitic English China Clay
(ECC). Three different concrete mixes with varying cement
content (c) and water–cement (w/c) ratio were used in the
investigation, and two of these (mix 1, c ¼ 290 kg/m3, w/c ¼0.75; mix 2, c ¼ 320 kg/m3, w/c ¼ 0.55) correspond to mixes
used by the Building Research Establishment (BRE) in a field
trial as described by Crammond and Halliwell (1998) and
Crammond et al. (2003). Mix 3 consists of 320 kg/m3 cement
with w/c ¼ 0.75. According to BRE Special Digest 1 (BRE,
2005) the design chemical (DC) class of mixes 1 and 3 is DC-1
and of mix 2 is DC-2. The cement type used was a Portland
cement CEM I 42.5 N with a C3A content of 8%. The mix
parameters were chosen to accelerate TSA at the interface.
To simulate underground conditions three different pressures (10,
40, 70 kN/m2) were applied to the interface. Two different casting
faces – top-cast and bottom-cast face – were in contact with the
clay. The top-cast surface represents precast (PC) conditions, and
the bottom cast face represents cast-in situ (CS) conditions,
simulating precast and cast in place piles respectively. In the case
of the PC condition the concrete was cast in the moulds, cured
and, after a curing time of 28 days, backfilled with the weathered
clay, whereas in the CS condition concrete was cast directly
against the clay. The specimens were stored in an environmental
chamber at a constant temperature of 68C for up to 27 months.
TSA-unaffected control specimens were tested at an age of
6 months. The variables investigated are summarised in Table 1.
2.3 Testing
The water content, pH value and mineralogical composition were
determined at distances of 0–10 mm, 10–20 mm, 20–30 mm,
30–40 mm and 40–50 mm from the interface. The water content
and pH value were measured according to BS 1377-3 (BSI, 1990).
The mineralogical composition of the clay samples was deter-
mined using the Siemens D5000 powder X-ray diffractometer
with a silicon powder standard. The main purpose of these tests
Concrete mix Applied pressure: kN/m2 Method of casting Clay type Storage solution
10 40 70 Precast In situ LLC ECC Sulfate Water
1 (290–0.75) 3 3 3 3 3 3 3 3 3
2 (320–0.55) 3 3 3 3 3 3 3 3
3 (320–0.75) 3 3 3 3 3 3 3
Table 1. Variables investigated
409
Geotechnical EngineeringVolume 166 Issue GE4
Chemical interactions at the concrete/clayinterface due to thaumasite form ofsulfate attackBrueckner, Williamson and Clark
was to identify the formation of brucite and thaumasite; changes
in the clay structure did not form part of the testing.
3. Chemical interactions
3.1 Macroscopical observations
Different macroscopic clay structures were observed during
sampling. The first approximately 10 mm of clay showed a friable
structure that was mostly separated by cracks from the main body
(Figures 1 and 2). This zone also appeared drier than the samples
further into the clay, but the moisture content was actually higher.
3.2 Water content
The typical moisture content distribution of the clay adjacent to
the interface is illustrated in Figure 3, where the figure for 5 mm
relates to the 0–10 mm zone of clay. The moisture content at the
interface was significantly increased compared with the relatively consistent moisture content measured away from the surface.
Slight differences in moisture content, caused by variation in
compaction, occurred; however, a direct relationship due to this
or the casting position was not clearly defined.
A slight difference in the interface moisture, depending on the
age of the specimens, was observed in the control specimens. The
interface moisture content of the 6 month old control specimens
ranged from 35% to 44% (average 39%), compared with the
average interface moisture content of 32.5% for the 27 month old
specimens. This confirms the observations made by Lee (2001)
that the interface water content decreases slightly with time.
In the shear strength tests, shearing occurred either at the zone of
clay with increased moisture content or directly at the interface,
which demonstrates the tendency of the failure surface to occur
in the higher-moisture-content, lower-strength clay.
3.3 pH values
The pH value was measured at the same distance from the
interface as the moisture content. It ranged from 9.3 to 11.2 and
from 10.3 to 11.1 at the interface for kaolinitic ECC and illitic
LLC respectively, and was found to vary with distance from the
interface as well as with storage age.
The pH distribution within LLC adjacent to the interface is
illustrated in Figure 4, which was typical for all the specimens
investigated, and no significant differences between the casting
positions occurred. The pH at the interface was high, and reduced
linearly inwards; however, the rate of reduction depended on the
age of the specimen. This is demonstrated in Figures 5 and 6 by
the significantly different pH-affected area observed for the
control specimens (at an age of 6 months) compared with the
18 month old specimens. The original natural pH of the LLC was
7.7 and that of the ECC 5.4.
The reduction of the pH to the natural soil value did not coincide
with the position at which the moisture content attained a
constant value, as was observed by Lee (2001). Both the moisture
Figure 1. Clay structure at clay/concrete interface, LLC
Figure 2. Clay structure at clay/concrete interface, ECC
20
25
30
35
40
45
50
0 10 20 30 40 50
Moi
stur
e co
nten
t: %
Distance from interface: mm
PC 10 kPaPC 40 kPaPC 70 kPaCS 10 kPaCS 40 kPaCS 70 kPa
Figure 3. Change in moisture content with distance from
interface, mix 3-LLC (290–0.75), 27 months
410
Geotechnical EngineeringVolume 166 Issue GE4
Chemical interactions at the concrete/clayinterface due to thaumasite form ofsulfate attackBrueckner, Williamson and Clark
and the pH were independent of each other, but both had the
same increasing trend towards the concrete.
The pH at the interface depended on clay type, where the LLC
illitic interface generated a pH range of 10.3–11.1 and at the
ECC kaolinitic interface the range was 9.5–10.0, which is less
favourable for TSA. Despite this, thaumasite formed at both
interfaces, but a higher level of deterioration was observed at the
ECC interface.
The increase of pH in the clay adjacent to concrete is attributed
to ion diffusion processes in which alkali (Naþ, Kþ) and hydroxyl
ions (OH�), within the concrete and soil pore solution culminate
in the flocculation of clay particles. This increases the friability of
the clay, as was observed on the specimens, and illustrated in
Figures 1 and 2. Furthermore, it appeared that the optimum
moisture content was increased and an increase of the strength
and stability occurred as a result of the presence of hydroxyl ions.
The conditions would favour solidification processes as a result of
pozzolanic reactions where C-S-H and C-A-H form in the clay.
3.4 Mineralogical changes
Mineralogical changes of the clay adjacent to the interface were
identified in the case of the ECC, compared with original clay
samples where traces of brucite were detected: see Figure 7.
However, it is assumed that it is more likely that this brucite was
derived from the thaumasite formation process at the interface
where, according to Crammond and Nixon (1993), it is frequently
observed. Further changes in the mineralogical composition
depending on the distance from the interface were not found.
Significant differences in the mineralogical composition between
the natural LLC and the LLC adjacent to the concrete were not
identified; see Figure 8. Therefore it is concluded that no signifi-
cant changes of the mineralogy of the clay at the interface
occurred using the Siemens D5000 powder X-ray diffractometer
(XRD), although the presence of swelling clays and any changes
within were not included in the XRD testing. Microscopic
investigations at the boundary concrete/thaumasite/clay confirmed
this, and no traces of TSA reaction products were found in the
clay using polarised light microscopy or XRD. Furthermore, no
differences in gypsum and pyrite concentrations were detected
using XRD. This is due to the extensive supply of sulfate ions
through the highly concentrated and aggressive magnesium
sulfate solution.
Mineralogical changes occurred within the thaumasite reaction
product layer adjacent to the clay during the investigation period.
Interfaces that were subject to an extensive thaumasite formation
of up to 24 mm after 27 months showed changes in the composi-
tion of the thaumasite layer, as is discussed in more detail by
Brueckner et al. (2012). The change in composition was visible
in the different appearances of the TSA layer, and is indicated
schematically in Figure 9. The older, reddish reaction layer zone,
which was in contact with the clay, was enriched with gypsum,
whereas the newly formed, greyish reaction products contained
less gypsum (Figure 10).
4. DiscussionThe water content and pH measurements of the clay adjacent to
the concrete confirmed the findings of several researchers,
including Chuang and Reese (1969), Lee (2001), Milititsky et al.
7·0
7·5
8·0
8·5
9·0
9·5
10·0
10·5
11·0
11·5
0 10 20 30 40 50
pH
Distance from interface: mm
Mix 3 PC (27 m)Mix 4 PC (27 m)Mix 3 CS (27 m)Mix 4 (27 m)CSMix 5 (27 m)CS
Figure 4. Change in pH value with distance from interface,
PC/CS-LLC
5
6
7
8
9
10
11
12
0 5 10 15 20 3025 40 45 50
pH
Distance from interface: mm35
Mix 3 controlMix 3 (18 m)Mix 3 (27 m)Mix 4 (27 m)
Figure 5. Change in pH value with distance from interface,
PC-ECC
5
6
7
8
9
10
11
12
0 5 10 15 20 25 30 35 40 45 50
pH
Distance from interface: mm
Mix 3 controlMix 3 (18 m)Mix 3 (27 m)Mix 4 (27 m)Mix 5 (27 m)
Figure 6. Change in pH value with distance from interface,
CS-ECC
411
Geotechnical EngineeringVolume 166 Issue GE4
Chemical interactions at the concrete/clayinterface due to thaumasite form ofsulfate attackBrueckner, Williamson and Clark
(1982), O’Neill and Reese (1970) and Yong (1979), that these
two parameters increase towards the concrete/soil interface. How-
ever, the measurements undertaken during this investigation did
not agree with the findings of Lee (2001) that water content and
pH reduce to constant values at approximately the same distance
from the interface. Water content and pH follow different trends,
although a similar trend occurs during the early stages after
construction, when the majority of chemical interactions between
concrete and soil take place. Groundwater becomes enriched with
hydroxyl and alkali ions from the concrete pore solution, which
5 10 15 20 25 30 35 40 45 502-Theta-scale
Pure ECC
Interface ECC
M
K
B
MQ
K
Q M�
C
MM K�
B
K
QM
Lin
(cou
nts)
Figure 7. Mineralogical composition of pure and interface ECC
clay: B, brucite; C, calcite; K, kaolinite; M, muscovite; Q, quartz
5 10 15 20 25 30 35 40 45 502-Theta-scale
Pure LLC
Interface LLC
GM
MQ
Q M�
A M Q M�P P
QM
Lin
(cou
nts)
C
Figure 8. Mineralogical composition of pure and interface LLC
clay: A, anorthoclase; C, calcite; G, gypsum; M, muscovite;
P, pyrite; Q, quartz
412
Geotechnical EngineeringVolume 166 Issue GE4
Chemical interactions at the concrete/clayinterface due to thaumasite form ofsulfate attackBrueckner, Williamson and Clark
increases the pH of the adjacent soil and causes solidification
processes. The ion exchange occurs mainly during the initial
months of the structure, and decreases gradually. This is due to
leaching or decalcification processes in the near-surface zone,
which depend on the bicarbonate content of the groundwater. The
density of the concrete pore structure in the surface layer
increases, and therefore the amounts of available hydroxyl and
alkali ions are reduced. This decreases the ion exchange mechan-
isms between concrete and soil and the pH at the interface is
reduced by the natural pH of the standing or flowing groundwater
due to diffusion.
The formation of thaumasite does not have an observable effect
on these two processes. The outer layer of concrete undergoes
continuous sulfate attack, which requires highly alkaline condi-
tions at the concrete surface to form stable thaumasite. However,
the pH-affected zone reduces gradually in the adjacent soil
towards the concrete/thaumasite/soil interface, and this contri-
butes to the decomposition of the thaumasite as observed at the
kaolinitic ECC interface in the pH value 9.7–10. It is suggested
that the pH gradient observed in the clay is also present within
the TSA layer, because the gypsum content decreased towards the
concrete surface. The pH drops below a threshold where the
stability of thaumasite significantly decreases, and the TSA layer
becomes enriched with gypsum.
The main reaction products found were thaumasite, ettringite,
quartz and calcite. In addition, gypsum was detected at the
boundary of the acidic ECC, whereas no increased amount of
gypsum was found at the LLC interface with a pH of 10.3–11.1.
The decomposition of thaumasite and ettringite in favour of
mainly gypsum within the formed reaction product layer at the
ECC interface (pH 9.7–10) supports the hypothesis of thaumasite
being an intermediate reaction product during TSA.
The formation of thaumasite does not affect the mineralogical
composition of the adjacent clay that could be detected using
XRD. Traces of brucite were found in the zone next to the
interface, but these could be associated with the formation of a
brucite layer at the thaumasite/soil interface. According to
Crammond and Nixon (1993), brucite is frequently observed at
the interface when concrete is exposed to magnesium-containing
solutions or groundwater.
5. ConclusionThe investigation of the chemical interactions at the concrete/clay
interface confirmed several trends reported in the literature, but
also showed disagreement with some previous findings. The
observations are based on findings from a concrete/clay interface
unaffected by TSA, and from an interface consisting of concrete/
thaumasite/clay. The conclusions of the investigations are listed
below.
j The clay within 10 mm of the interface is more friable than
elsewhere, despite having an increased moisture content,
which is caused by flocculation of clay particles.
j Within a distance of 10–15 mm from the concrete the
moisture content increases towards the interface; however, the
increase decreases with time.
j The pH increases towards the interface, but both the zone
affected by increased pH and the increase in pH itself
decrease with time.
j A relationship between moisture content and pH was not
apparent.
j The mineralogical composition of the TSA reaction product
layer changes close to the interface. The older TSA layer
close to the clay is enriched in gypsum, which is due to the
decomposition of thaumasite and ettringite in favour of
mainly gypsum with time.
j The pH gradient continues within the TSA reaction product
layer up to the unattacked concrete surface.
j Changes in the clay mineralogy due to TSA were not detected
within the clay adjacent to the interface.
Gypsum-rich reddish layer
Gypsum-poor greyish layer
Figure 9. Structure of TSA layers
60
50
40
30
20
10
0
Min
eral
con
cent
ratio
n: %
Calcite Quartz Thaumasite Ettringite Gypsum
Greyish
Reddish
Figure 10. Mineralogical composition of TSA layers
413
Geotechnical EngineeringVolume 166 Issue GE4
Chemical interactions at the concrete/clayinterface due to thaumasite form ofsulfate attackBrueckner, Williamson and Clark
AcknowledgementsThe senior author is very grateful to the Engineering and Physical
Sciences Research Council (EPSRC), who funded this research
project, and to the University of Birmingham.
REFERENCES
Brueckner R (2008) Accelerating the Thaumasite Form of Sulfate
Attack and an Investigation of its Effects on Skin Friction.
PhD thesis, University of Birmingham, Birmingham, UK.
Brueckner R, Williamson SJ and Clark LA (2012) The effects of
the thaumasite form of sulfate attack on skin friction at the
concrete/clay interface. Cement and Concrete Research 42(2):
424–430.
BRE (2005) Concrete in Aggressive Ground. Building Research
Establishment, Watford, UK, Special Digest 1.
BSI (1990) BS 1377-3: Methods of test for soils for civil
engineering purposes. Chemical and electro-chemical tests.
British Standards Institution, Milton Keynes, UK.
Cernica JN (1995) Geotechnical Engineering: Soil Mechanics.
Wiley, New York, NY, USA.
Chuang JW and Reese LC (1969) Studies of Shearing Resistance
Between Cement Mortar and Soil. University of Texas at
Austin, Austin, TX, USA. Research report 89-3.
Crammond NJ and Halliwell MA (1998) The Thaumasite Field
Trial, Shipston-on-Stour: Details of the Site and Specimen
Burial. Building Research Establishment, Watford, UK,
Client Report CR68/94.
Crammond NJ and Nixon PJ (1993) Deterioration of concrete
foundation piles as a result of thaumasite formation.
Proceedings of the 6th International Conference on
Durability Building of Materials, Tokyo, Japan, vol. 1,
pp. 295–305.
Crammond NJ, Collet GW and Longworth TI (2003) Thaumasite
field trial at Shipston-on-Stour: three-year preliminary
assessment of buried concretes. Cement and Concrete
Composites 25(8): 1035–1043.
El-Rawi NM and Awad AA (1981) Permeability of lime stabilized
soils. Transportation Engineering Journal 107(1): 25–35.
Hill J, Byars EA, Sharp JH, Lynsdale CJ, Cripps JC and Zhou Q
(2003) An experimental study of combined acid and sulfate
attack of concrete. Cement and Concrete Composites 25(8):
997–1003.
Lee L (2001) Soil–Pile Interaction of Bored and Cast In-Situ
Piles. PhD thesis, University of Birmingham, Birmingham,
UK.
Milititsky J, Jones JR and Clayton CRI (1982) A radiochemical
method of studying the moisture movement between fresh
concrete and clay. Geotechnique 32(3): 271–275.
O’Neill MW and Reese LC (1970) Behaviour of Axially Loaded
Drilled Shafts in Beaumont Clay. University of Texas at
Austin, Austin, TX, USA, Research report 89-8.
Sherwood PT (1993) Soil Stabilisation with Cement and Lime.
HMSO, London, UK.
Slater D, Floyd M and Wimpenny DE (2003) A summary of the
Highways Agency Thaumasite Investigation in
Gloucestershire: the scope of work and main findings.
Cement and Concrete Composites 25(8): 1067–1076.
Webster JD and Sheary VJ (1962) Stabilisation of Clays and
other Fine Grained Materials. Australian Road Research
Board, Vermont South, Victoria, Australia, vol. 1, part 2, pp.
223–250.
Yong KY (1979) A Laboratory Study of the Shaft Resistance of
Bored Piles. PhD thesis, University of Sheffield, Sheffield,
UK.
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Chemical interactions at the concrete/clayinterface due to thaumasite form ofsulfate attackBrueckner, Williamson and Clark