6
Plastic shrinkage cracking of blended cement concretes in hot environments A. A. Almussalam, M. Maslehuddin, M. Abdul-Waris, F. H. Dakhil and O. S. B. Al-Amoudi King Fahd University of Petroleum and Minerals This paper reports results of a study conducted to evaluate plastic shrinkage cracking of concrete made with varying dosages of several pozzolanic materials, such as fly ash (20, 30 and 40%), silica fume (5, 10 and 15%) and blastfurnace slag (50, 60 and 70%). These concrete specimens were exposed to hot–humid and hot–dry environ- ments. The effect of these environmental conditions on plastic shrinkage cracking was evaluated. The rate of water evaporation in the blended cement concrete specimens was noted to be more than that in the plain cement concrete specimens. Further, bleeding in the blended cement concrete specimens was less than that in plain cement concrete specimens. The cumulative effect of these two parameters resulted in increased plastic shrinkage cracking of the blended cement concretes. Although cracks were observed earlier in the plain cement concrete specimens than in the blended cement concrete specimens, the total area of cracks in the latter cements was more than that in the former cements. The results of this study also indicate that relative humidity influences plastic shrinkage cracking of concrete significantly in comparison with the effect of the type of cement. Introduction Industrial by-products, such as fly ash, silica fume and blastfurnace slag, are increasingly used worldwide to produce dense and impermeable concrete. In coun- tries where these materials are available, as waste pro- ducts, their use in concrete not only enhances its durability but also decreases its cost. Other benefits of using these materials, in such situations, include con- servation of energy required for the production of ce- ment, and environmental protection. However, in countries where these materials are not available lo- cally, the cost of importing them is often more than the cost of ordinary Portland cement. In such situations, these materials are utilized purely for technical reasons related to improvement in concrete durability. While these materials have been beneficially utilized to im- prove concrete durability and reduce the heat of hydra- tion in mass concrete, concerns have been voiced by several investigators about the need for continued and enhanced curing. 1–3 This aspect is of particular concern in the arid and semi-arid areas of the world, where high temperature or low humidity favours rapid evaporation of mixing and curing water. In such situations, insuffi- cient moisture available for the pozzolanic reaction may lead to decreased hydration of the cement as com- pared to ordinary Portland cement. Further, rapid eva- poration of water accelerates plastic shrinkage of concrete, which, if restrained, leads to its cracking. These cracks, which are often very fine, are difficult to repair and accelerate the diffusion of aggressive agents into the concrete mass, thereby resulting in an en- hanced risk of premature deterioration of the concrete. The possibility of plastic shrinkage cracking in blended cements, in hot and/or arid environments, is also enhanced as these environmental conditions encou- rage rapid evaporation of water, leading to (i) insuffi- cient moisture for the pozzolanic reaction and (ii) a decrease in the tensile strain capacity of concretes made using these cements. Therefore, preventive meas- ures should be adopted when such materials are used in hot–arid environments. 4 Fly ash and granulated blast- furnace slag cements are recommended in hot climates for the production of durable concrete. 5 According to Cohen et al., 6 the higher surface area of silica fume particles increases the capillary pressure and conse- Magazine of Concrete Research, 1999, 51, No. 4, Aug., 241–246 241 0024-9831 # 1999 Thomas Telford Ltd King Fahd University of Petroleum and Minerals, Dhahran 31261, Saudi Arabia. (MCR 708) Paper received 13 May 1998; last revised 13 October 1998; accepted 3 February 1999

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Plastic shrinkage cracking of blended cement

concretes in hot environments

A. A. Almussalam,� M. Maslehuddin,� M. Abdul-Waris,� F. H. Dakhil� andO. S. B. Al-Amoudi�

King Fahd University of Petroleum and Minerals

This paper reports results of a study conducted to evaluate plastic shrinkage cracking of concrete made with

varying dosages of several pozzolanic materials, such as fly ash (20, 30 and 40%), silica fume (5, 10 and 15%) and

blastfurnace slag (50, 60 and 70%). These concrete specimens were exposed to hot±humid and hot±dry environ-

ments. The effect of these environmental conditions on plastic shrinkage cracking was evaluated. The rate of water

evaporation in the blended cement concrete specimens was noted to be more than that in the plain cement concrete

specimens. Further, bleeding in the blended cement concrete specimens was less than that in plain cement concrete

specimens. The cumulative effect of these two parameters resulted in increased plastic shrinkage cracking of the

blended cement concretes. Although cracks were observed earlier in the plain cement concrete specimens than in

the blended cement concrete specimens, the total area of cracks in the latter cements was more than that in the

former cements. The results of this study also indicate that relative humidity influences plastic shrinkage cracking

of concrete significantly in comparison with the effect of the type of cement.

Introduction

Industrial by-products, such as fly ash, silica fume

and blastfurnace slag, are increasingly used worldwide

to produce dense and impermeable concrete. In coun-

tries where these materials are available, as waste pro-

ducts, their use in concrete not only enhances its

durability but also decreases its cost. Other benefits of

using these materials, in such situations, include con-

servation of energy required for the production of ce-

ment, and environmental protection. However, in

countries where these materials are not available lo-

cally, the cost of importing them is often more than the

cost of ordinary Portland cement. In such situations,

these materials are utilized purely for technical reasons

related to improvement in concrete durability. While

these materials have been beneficially utilized to im-

prove concrete durability and reduce the heat of hydra-

tion in mass concrete, concerns have been voiced by

several investigators about the need for continued and

enhanced curing.1±3

This aspect is of particular concern

in the arid and semi-arid areas of the world, where high

temperature or low humidity favours rapid evaporation

of mixing and curing water. In such situations, insuffi-

cient moisture available for the pozzolanic reaction

may lead to decreased hydration of the cement as com-

pared to ordinary Portland cement. Further, rapid eva-

poration of water accelerates plastic shrinkage of

concrete, which, if restrained, leads to its cracking.

These cracks, which are often very fine, are difficult to

repair and accelerate the diffusion of aggressive agents

into the concrete mass, thereby resulting in an en-

hanced risk of premature deterioration of the concrete.

The possibility of plastic shrinkage cracking in

blended cements, in hot and/or arid environments, is

also enhanced as these environmental conditions encou-

rage rapid evaporation of water, leading to (i) insuffi-

cient moisture for the pozzolanic reaction and (ii) a

decrease in the tensile strain capacity of concretes

made using these cements. Therefore, preventive meas-

ures should be adopted when such materials are used in

hot±arid environments.4

Fly ash and granulated blast-

furnace slag cements are recommended in hot climates

for the production of durable concrete.5

According to

Cohen et al.,6

the higher surface area of silica fume

particles increases the capillary pressure and conse-

Magazine of Concrete Research, 1999, 51, No. 4, Aug., 241±246

241

0024-9831# 1999 Thomas Telford Ltd

� King Fahd University of Petroleum and Minerals, Dhahran 31261,

Saudi Arabia.

(MCR 708) Paper received 13 May 1998; last revised 13 October

1998; accepted 3 February 1999

quently, makes concrete more vulnerable to plastic

shrinkage cracking. However, no data are available on

plastic shrinkage cracking of blended cement concretes

in hot and arid environments. This is understandable, as

these materials have only been recently introduced in

these regions. Such a study will be helpful, firstly, to

clarify the concerns often raised regarding enhanced

plastic shrinkage of blended cement concretes in hot

and arid regions of the world, and, secondly, in planning

preventive methodologies.

This investigation was conducted to evaluate the

effect of hot±arid (temperature 458C and relative hu-

midity 25%) and hot±humid (temperature 458C and

relative humidity 95%) conditions on plastic shrinkage

cracking in blended cement concretes made using fly

ash, blastfurnace slag and silica fume. Commonly used

dosages of these materials were used to produce

blended cement concretes. For comparison purposes,

plain cement concrete specimens were also exposed to

similar temperature and humidity conditions.

Experimental programme

Materials

Plain cement concrete specimens were made using

ASTM C 150 Type V cement. Silica fume cement con-

crete specimens were made with 5, 10 and 15% silica

fume, which was used as a replacement for cement. In

the fly ash cement concrete specimens, 20, 30 and 40%

cement was replaced with fly ash. The blastfurnace slag

cement concrete specimens contained 50, 60 and 70%

blast furnace slag, and Type V cement constituted the

remaining bulk of the cementitious material. Table 1

shows a composition of Type V cement and the pozzo-

lanic materials used in this study.

The concrete specimens were made with a cementi-

tious materials content of 350 kg=m3 and an effective

water-to-cementitious-materials ratio of 0´40. Crushed

limestone, with a bulk specific gravity of 2´46 and

water absorption of 3´0%, was used as coarse aggre-

gate. Dune sand with a specific gravity of 2´54 and

water absorption of 0´23% was used as fine aggregate.

Table 2 shows the grading of coarse and fine aggregate.

All the concrete mixtures were designed for a work-

ability of 50±75 mm slump. A suitable dosage of Con-

plast 430, a high-range water reducer, was used to

obtain the desired workability.

Specimens and test procedures

Concrete slab specimens measuring 450 3 450 320 mm were cast to evaluate the effect of exposure

conditions on plastic shrinkage cracking. The thickness

of the concrete specimens was selected to represent a

large surface-area-to-volume ratio, typically that of a

concrete slab. The concrete specimens were cast in a

controlled temperature±humidity chamber. The re-

quired temperature was maintained using electric hea-

ters and a temperature controller. The relative humidity

was controlled through a commercial humidifier and

dehumidifier system.

The concrete specimens were cast in moulds made of

aluminium and Plexiglas. These forms reduce the ab-

sorption of moisture from the fresh concrete. This cre-

ates uniform conditions among all the tests, increases

bleeding and forces a one-dimensional water move-

ment, and the base provides a restraint encouraging

plastic shrinkage cracking. The concrete constituents

were mixed in an electrically operated concrete mixer

and then poured into the moulds, which were covered

with plastic sheets, and consolidated on a vibrating

table and levelled by a straight edge without sideways

or swaying motion. The concrete specimens were then

exposed to the desired temperature and humidity condi-

tions (temperature of 458C and RH of 25 or 95%).

Bleeding in plain and blended cement concrete spe-

cimens was evaluated by casting these mixtures in a

yield bucket, as recommended by ASTM C 232 Meth-

od A, and covered with a plastic sheet. The bleeding

water was collected using a pipette at 10 min intervals

during the first 40 min and then at intervals of 30 min

till cessation of bleeding.

The water evaporation was expressed as a percentageTable 1. Chemical analysis of cement and blending materials:

weight %

Constituent Type V Silica

fume

Fly ash Blastfurnace

slag

SiO2 22´20 92´7 52´3 31´51

Al2O3 3´48 0´29 23´4 17´23

Fe2O3 3´88 0´27 4´20 0´49

CaO 65´05 0´32 12´5 36´63

MgO 2´20 0´92 Ð 11´27

SO3 1´85 Ð 0´64 Ð

K2O 0´28 0´99 Ð 0´62

Na2O 0´15 0´33 Ð Ð

Loss on Ignition 0´80 2´71 0´26 Ð

C3S 62´00 Ð Ð Ð

C2S 17´00 Ð Ð Ð

C3A 2´70 Ð Ð Ð

C4AF 11´80 Ð Ð Ð

Table 2. Aggregate grading

Sieve opening: mm Percentage passing

Coarse aggregate Fine aggregate

12´50 100 Ð

9´50 100 Ð

4´75 60 Ð

2´36 20 Ð

1´18 5 100

0´6 0 86

0´425 Ð 64

0´30 Ð 43

0´15 Ð 18

0´075 Ð 1

Almussalam et al.

242 Magazine of Concrete Research, 1999, 51, No. 4

of water evaporated and the rate of evaporation. The

percentage of water evaporated was calculated as the

ratio of water evaporated to the total water added to the

mix, while the rate of evaporation was evaluated by

dividing the water evaporated in 6 h by the surface area

of the slab, i.e. 450 3 450 mm2. The change in weight

of the concrete mix, due to water evaporation, was

recorded at periodic intervals, up to 6 h by placing the

mould filled with concrete on a digital balance of 0´1 g

sensitivity.

Plastic shrinkage cracking was evaluated by monitor-

ing the time to initiation of cracks and their area. Both

the length and average width of cracks were recorded

and the total area of cracks was expressed as a propor-

tion of the surface area of the slab, i.e. 450 3 450 mm2.

Results and discussion

Quantity of water evaporated

Figures 1±3 show the quantity of water evaporated

from the plain and blended cement concrete specimens

exposed to a temperature of 458C and an RH of 25 and

95%. Fig. 1 shows the effect of relative humidity on

water evaporation in plain and blastfurnace slag (BFS)

cement concrete specimens. The quantity of water eva-

porated from the plain cement concrete specimens was

less than that from the BFS cement concrete specimens.

The quantity of water evaporated increased with the

quantity of blastfurnace slag. The quantity of water

evaporated from the plain cement concrete specimens,

exposed to an RH of 95%, was 2´6%, while it was 9´2,

10´4 and 11´9% in the BFS cement concrete specimens

containing 50, 60 and 70% slag, respectively. In the

BFS cement concrete specimens exposed to an RH of

25% these values were 45´9, 48´4 and 49´9%, respec-

tively, while in the plain cement concrete specimens

the quantity of water evaporated was 41´4%.

Figure 2 shows the effect of relative humidity on

water evaporation in silica fume and plain cement con-

crete specimens. In these specimens also, the quantity

of water evaporated increased with the silica fume con-

tent. The water evaporated from the concrete specimens

exposed to an RH of 25% was in the range of 41 to

45%. While 2´6% water evaporated from the plain ce-

ment concrete specimens exposed to a relative humidity

of 95%, the water evaporated from 5, 10 and 15% silica

fume concrete specimens, exposed to a similar temp-

erature and relative humidity, was 5´2, 13´5 and 14´2%,

respectively.

Figure 3 depicts the effect of relative humidity on

water evaporation in fly ash and plain cement concrete

specimens. In 0, 20, 30 and 40% fly ash cement con-

crete specimens, exposed to an RH of 25%, the quan-

tity of water evaporated was 41´1, 44´1, 46´6 and

46´6%, respectively. In the plain cement concrete speci-

mens, exposed to an RH of 95%, 2´6% water evapo-

rated, while 8´9, 12´5 and 15´3% water evaporated from

20, 30 and 40% fly ash cement concrete specimens,

respectively.

Figure 4 depicts the rate of water evaporation in the

plain and BFS cement concrete specimens. As ex-

pected, the rate of evaporation increased with the quan-

tity of blastfurnace slag. In the plain cement concrete

specimens, exposed to an RH of 25%, the rate of water

evaporation was 0´37 kg=m2 per hour, while this rate

was 0´42, 0´44 and 0´45 kg=m2 per hour in the 50, 60

and 70% BFS cement concrete specimens, respectively.

The rate of water evaporation in the concrete specimens

50

45

40

35

30

25

20

15

10

5

0

Qua

ntity

of w

ater

eva

pora

ted:

%

RH 25% RH 95%

Type V 10% SF

5% SF 15% SF

Fig. 2. Quantity of water evaporated from plain and silica

fume (SF) cement concretes

50

45

40

35

30

25

20

15

10

5

0

Qua

ntity

of w

ater

eva

pora

ted:

%

RH 25% RH 95%

Type V 60% BFS

50% BFS 70% BFS

Fig. 1. Quantity of water evaporated from plain and blastfur-

nace slag cement concretes

50

45

40

35

30

25

20

15

10

5

0

Qua

ntity

of w

ater

eva

pora

ted:

%

RH 25% RH 95%

Type V 30% FA

20% FA 40% FA

Fig. 3. Quantity of water evaporated from plain and fly ash

(FA) cement concretes

Plastic shrinkage cracking in hot environments

Magazine of Concrete Research, 1999, 51, No. 4 243

exposed to an RH of 95% was less than that in the

concrete specimens exposed to an RH of 25%. The rate

of evaporation in the plain cement concrete specimens

was 0´024 kg=m2 per hour, while it was in the range of

0´08 to 0´11 kg=m2 per hour in the BFS cement con-

crete specimens.

Figure 5 shows the effect of relative humidity on the

rate of water evaporation in the silica fume cement

concrete specimens. In the concrete specimens exposed

to an RH of 25%, the rate of water evaporation was in

the range of 0´37 to 0´41 kg=m2 per hour. The rate of

water evaporation in the plain cement concrete speci-

mens exposed to an RH of 95% was 0´024 kg=m2 per

hour, while it was 0´047, 0´122 and 0´129 kg=m2 per

hour in the 5, 10 and 15% silica fume cement concrete

specimens, respectively.

Figure 6 shows the rate of water evaporation in the

plain and fly ash cement concrete specimens. The rate

of water evaporation in the plain cement concrete spe-

cimens exposed to an RH of 25% was slightly less than

that in the fly ash cement concrete specimens exposed

to a similar relative humidity. This difference, however,

became more distinct in the concrete specimens ex-

posed to an RH of 95%. The rate of evaporation in the

plain cement concrete specimens exposed to an RH of

95% was nearly 0´024 kg=m2 per hour and it was in the

range of 0´08 to 0´14 kg=m2 per hour in the fly ash

cement concrete specimens. In the fly ash cement con-

crete specimens exposed to an RH of 25% the rate of

evaporation was in the range of 0´4 to 0´42 kg=m2 per

hour.

The data in Figs 4±6 indicate that the rate of eva-

poration in the blended cement concrete specimens was

more than that in the plain cement concrete specimens,

particularly when they were exposed to high relative

humidity. When the humidity was low, e.g. 25%, the

severity of the exposure conditions outweighed the in-

fluence of cement type.

Time to initiation and total area of cracks

Table 3 summarizes the time to initiation of cracks

and their total area in plain and blended cement con-

crete specimens exposed to an RH of 25%. Blastfur-

nace slag cement concrete specimens cracked later than

plain cement concrete specimens. Further, the time to

initiation of cracks increased with the quantity of BFS.

Cracks were observed in the plain cement concrete

specimens after 3´5 h, while they were observed after 4,

4 and 4´5 h in the 50, 60 and 70% BFS cement con-

crete specimens, respectively. In the fly ash cement

concrete specimens, also, the time to crack initiation

increased with the quantity of fly ash. Cracks were

0.5

0.45

0.4

0.35

0.3

0.25

0.2

0.15

0.1

0.05

RH 25% RH 95%

Type V

60% BFS

50% BFS

70% BFS

Rat

e of

eva

pora

tion:

kg/

m2

per

hour

0

Fig. 4. Rate of evaporation in plain and blastfurnace slag

cement concretes

0.45

0.4

0.35

0.3

0.25

0.2

0.15

0.1

0.05

0RH 25% RH 95%

Type V 10% SF

5% SF 15% SF

Rat

e of

eva

pora

tion:

kg/

m2

per

hour

Fig. 5. Rate of evaporation in plain and silica fume cement

concretes

0.45

0.4

0.35

0.3

0.25

0.2

0.15

0.1

0.05

0RH 25% RH 95%

Type V 30% FA

20% FA 40% FA

Rat

e of

eva

pora

tion:

kg/

m2

per

hour

Fig. 6. Rate of evaporation in plain and fly ash cement con-

cretes

Table 3. Time to cracking and total area of cracks in plain

and blended cement concrete specimens exposed to a tem-

perature of 458C and RH of 25%

Type of cement Time to cracking:

h

Total area of

cracks: %

Plain 3´5 0´035

5% silica fume 3´5 0´041

10% silica fume 3´5 0´039

15% silica fume 4´0 0´046

20% fly ash 3´5 0´052

30% fly ash 4´0 0´05

40% fly ash 4´5 0´048

50% blastfurnace slag 4´0 0´079

60% blastfurnace slag 4´0 0´068

70% blastfurnace slag 4´5 0´052

Almussalam et al.

244 Magazine of Concrete Research, 1999, 51, No. 4

observed after 3´5, 4 and 4´5 h in the 20, 30 and 40%

fly ash cement concrete specimens, respectively. Cracks

were observed after 3´5 h in the 5 and 10% silica fume

cement concrete specimens, while in the 15% silica

fume cement concrete specimens they were noted after

4 h.

Cracks were not noted in the concrete specimens

exposed to an RH of 95%, except in the plain and 5%

silica fume cement concrete specimens. In the plain

cement concrete specimens cracks were observed after

6 h, while they were noted after 5´5 h in the 5% silica

fume cement concrete specimens.

As shown in Table 3, the total area of cracks in the

blended cement concrete specimens was more than that

in the plain cement concrete specimens. The total area

of cracks in 0, 50, 60 and 70% BFS cement concrete

specimens was 0´026, 0´079, 0´068 and 0´052%, respec-

tively. The increased area of cracks in the BFS cement

concrete specimens may be attributed to the low tensile

strain capacity of BFS cement concrete compared to

plain cement concrete at early ages. The total area of

cracks in the fly ash cement concrete specimens was

also more than that in the plain cement concrete speci-

mens. The total area of cracks in the 0, 20, 30 and 40%

fly ash cement concrete specimens was 0´026, 0´052,

0´050 and 0´048%, respectively. The total area of cracks

in the 0, 5, 10 and 15% silica fume cement concrete

specimens was 0´026, 0´041, 0´039 and 0´046%, respec-

tively.

As stated earlier, cracks were not observed in the

concrete specimens exposed to an RH of 95%, except

in the plain and 5% silica fume cement concrete speci-

mens. The total area of cracks in these specimens was

0´006 and 0´018%, respectively.

Bleeding

Figure 7 shows the cumulative bleed water in the

plain and blended cement concrete specimens. Maxi-

mum bleeding was measured in the plain cement con-

crete specimens. The bleeding was in the range of 1´19

to 1´74% in the silica fume cement concrete specimens,

while in fly ash and BFS cement concrete specimens it

was in the range of 0´9 to 1´56% and 1´51 to 1´73%,

respectively. The bleeding was 1´86% in the plain ce-

ment concrete specimens.

In general, the data obtained in this study indicate

that the total area of cracks, due to plastic shrinkage,

was more in blended cement concretes than in plain

cement concrete. This may be attributed to the lower

bleeding and higher rate of evaporation noted in

blended cement concrete. While cracks were observed

earlier in plain cement concrete, the total area of cracks

in these specimens was less than that in the blended

cement concrete specimens. Among the blended ce-

ments investigated, the total area of cracks in the blast-

furnace slag cement concrete was more than that in the

fly ash and silica fume cement concretes. This may be

attributed to the low tensile strain capacity of this ce-

ment compared to other cements, particularly at earlier

ages.

Another important finding of this study is the influ-

ence of relative humidity on factors controlling plastic

shrinkage cracking. The relative humidity considerably

influenced the rate of evaporation. The rate of evapora-

tion in both plain and blended cement concrete speci-

mens exposed to an RH of 95% was very low

compared to that in the specimens exposed to an RH of

25%. While the rate of evaporation in plain and

blended cement concrete specimens exposed to an RH

of 25% was in the range of 0´37 to 0´45 kg=m2 per

hour, it was in the range of 0´024 to 0´138 kg=m2 per

hour in the concrete specimens exposed to an RH of

95%. Since cracks were more predominant in the speci-

mens exposed to an RH of 25% it should be noted that

plastic shrinkage cracks can occur even when the rate

of evaporation is less than 1 kg=m2 per hour, a value

suggested by ACI 305.7

A similar phenomenon was

noted by the authors in plain cement concrete speci-

mens made with varying cement content and water±

cement ratio8

and in concrete specimens exposed to

different environmental conditions.9±11

Cracks were not observed in the concrete specimens

exposed to an RH of 95%, the exception being the

plain and 5% silica fume cement concrete specimens,

though the intensity of cracks in these concrete speci-

mens was very minimal. These results indicate that

relative humidity significantly influences plastic shrink-

age cracking in hot environments. Therefore, it is ne-

cessary to keep the environment humid to utilize the

technical advantages of using supplementary cementing

materials in concrete. This could be achieved by apply-

ing a curing compound after the completion of finish-

ing operations. Alternatively, the environment can be

kept humid by using a mist spray.

Conclusions

The rate of evaporation and the area of cracks in the

blended cement concrete specimens exposed to a tem-

perature of 458C and a relative humidity of 25% were

3.5

3

2.5

2

1.5

1

0.5

0

Type V

10% SF

5% SF

15% SF

20% FA

30% FA

40% FA

50% BFS

60% BFS

70% BFS

Tota

l ble

ed w

ater

: %

Fig. 7. Bleeding in plain and blended cement concretes

Plastic shrinkage cracking in hot environments

Magazine of Concrete Research, 1999, 51, No. 4 245

more than those in plain cement concrete specimens

exposed to similar temperature and humidity. Even

though cracks were noted earlier in plain cement con-

crete specimens, the total area of cracks in the blended

cement concrete specimens was more than that in plain

cement concrete specimens.

The total area of cracks in the blastfurnace slag ce-

ment concrete specimens was more than that in the

other blended and plain cement concrete specimens

exposed to a temperature of 458C and relative humidity

of 25%. The increase in the area of cracks in the BFS

cement concrete may be attributed to the low tensile

strain capacity of this cement, compared to other ce-

ments, particularly at early ages.

The relative humidity significantly influenced the

plastic shrinkage cracking of concrete. The rate of

evaporation in both plain and the blended cement con-

crete specimens exposed to a temperature of 458C and

a relative humidity of 95% was less than that in the

concrete specimens exposed to a similar temperature

but an RH of 25%. Cracks were not observed in the

cement concrete specimens exposed to an RH of 95%.

Although cracks were observed in plain and 5% silica

fume cement concrete specimens exposed to this hu-

midity, their intensity was very low.

The data obtained in this study indicate that relative

humidity influences plastic shrinkage cracking signifi-

cantly in comparison with the effect of the type of

cement. Therefore, to avoid plastic shrinkage cracking

in plain and blended cement concretes, particularly the

latter, the environment should be kept adequately moist,

especially in hot environments. This can be achieved

by applying a curing compound after the completion of

finishing operations or by keeping the environment

humid, for at least 6 h, by the use of a mist spray.

Acknowledgements

The support provided by the Department of Civil

Engineering and the Center for Engineering Research,

King Fahd University of Petroleum and Minerals,

Dhahran, Saudi Arabia, is gratefully acknowledged.

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246 Magazine of Concrete Research, 1999, 51, No. 4