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CEMENT and CONCRETE RESEARCH. Vol. 19, pp. 868-878, 1989. Printed in the USA. 0008-8846/89. $3.00+00. Copyright (c) 1989 Pergamon Press plc. EFFECT OF MIXING AND CURING WATERS ON THE BEHAVIOUR OF CEMENT PASTES AND CONCRETE PART I : MICROSTRUCTURE OF CEMENT PASTES H.Y.Ghorab~, M.S.HilaI~S and E.A.Kishar~ Cement Chemistry Laboratory, University College for Girls, Ain Shams University, Heliopolis, Cairo, Egypt ~ Structural Engineering Department, Faculty of Engineering Cairo University, Egypt (Communicated by F.W. Locher) (Received Dec. 31, 1988) ABSTRACT The influence of Sea, ground, Nile and drinking waters on the microstructure of some hydraulic cements is investigated by means of X-ray diffraction analysis. The calcium sulfo- and carboalumi- nate hydrates form well with a water cement ratio of 2. Seawater leads to the precipitation of gypsum. The hydration products of ordinary portland cement (OPC) pastes hydrated for a year with the four water types are similar. A survey on the analysis of waters used is given. Introduction The suitability of use of natural waters for mixing and curing cement mortars and concrete has been especially questioned in our country because of the increasing construction projects in remote areas where difficulties are encountered for the supply of soft water. The effect of seawater, when used for mixing, on the cement pastes and concrete was found to be compatible with most ac- celerators (i). It reduces the thickening time, enhances the hydration process and the consecutive strength development but retards the late strength (1,2). Well waters with up to I000 ppm S03 and 500 ppm chloride can be used for mixing mortar and con- crete (3) and ground water is recommended for concrete construc- tion with a maximum limit of 300 ppm chloride and 300 ppm S04(4). Mixing of OPC with slag, fly ash or other blended additives im- proves the performance of cement towards the sulfate attack (5,b) The effect of seawater on the cement and concrete is seen to be generally more worked out in the literature as compared to other types of natural water. The nature of these waters varies from one country to the other depending on the nature of the 868
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EFFECT OF MIXING AND CURING WATERS ON THE BEHAVIOUR OF CEMENT PASTES AND CONCRETE PART I : MICROSTRUCTURE OF CEMENT PASTES

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Page 1: EFFECT OF MIXING AND CURING WATERS ON THE BEHAVIOUR OF CEMENT PASTES AND CONCRETE PART I : MICROSTRUCTURE OF CEMENT PASTES

CEMENT and CONCRETE RESEARCH. Vol. 19, pp. 868-878, 1989. Printed in the USA. 0008-8846/89. $3.00+00. Copyright (c) 1989 Pergamon Press plc.

EFFECT OF MIXING AND CURING WATERS ON THE BEHAVIOUR OF CEMENT PASTES AND CONCRETE

PART I : MICROSTRUCTURE OF CEMENT PASTES

H.Y.Ghorab~, M .S .H i l a I~S and E .A .K ishar~ Cement Chemistry L a b o r a t o r y , U n i v e r s i t y C o l l e g e f o r G i r l s ,

Ain Shams U n i v e r s i t y , H e l i o p o l i s , C a i r o , Egypt ~ S t r u c t u r a l Eng inee r i ng Department, F a c u l t y o f Eng inee r ing

Ca i ro U n i v e r s i t y , Egypt

(Communicated by F.W. Locher) (Received Dec. 31, 1988)

ABSTRACT The i n f l u e n c e o f Sea, ground, N i l e and d r i n k i n g waters on the m i c r o s t r u c t u r e o f some h y d r a u l i c cements i s i n v e s t i g a t e d by means o f X-ray d i f f r a c t i o n a n a l y s i s . The ca lc ium s u l f o - and c a r b o a l u m i - na te hydra tes form w e l l w i t h a water cement r a t i o o f 2. Seawater leads to the p r e c i p i t a t i o n o f gypsum. The h y d r a t i o n products of o r d i n a r y p o r t l a n d cement (OPC) pastes hydra ted f o r a year w i t h the f o u r water types are s i m i l a r . A survey on the a n a l y s i s of waters used i s g i v e n .

I n t r o d u c t i o n

The s u i t a b i l i t y o f use o f n a t u r a l waters f o r m ix ing and c u r i n g cement mor ta rs and conc re te has been e s p e c i a l l y ques t ioned in our coun t r y because o f the i n c r e a s i n g c o n s t r u c t i o n p r o j e c t s in remote areas where d i f f i c u l t i e s are encountered f o r the supply of s o f t wa te r .

The e f f e c t o f seawater , when used f o r m i x i n g , on the cement pastes and conc re te was found to be compa t i b l e w i t h most ac- c e l e r a t o r s ( i ) . I t reduces the t h i c k e n i n g t ime , enhances the h y d r a t i o n process and the c o n s e c u t i v e s t r e n g t h development but r e t a r d s the l a t e s t r e n g t h ( 1 , 2 ) . Well waters w i t h up to I000 ppm S03 and 500 ppm c h l o r i d e can be used f o r m ix ing mor ta r and con- c r e t e (3) and ground water i s recommended f o r conc re te c o n s t r u c - t i o n w i t h a maximum l i m i t o f 300 ppm c h l o r i d e and 300 ppm S04(4). M ix ing o f OPC w i t h s l a g , f l y ash or o t h e r blended a d d i t i v e s im- proves the performance o f cement towards the s u l f a t e a t t a c k (5 ,b)

The e f f e c t o f seawater on the cement and conc re te i s seen to be g e n e r a l l y more worked ou t in the l i t e r a t u r e as compared to o t h e r types o f n a t u r a l wa te r . The n a t u r e of these waters v a r i e s from one coun t r y to the o t h e r depending on the n a t u r e of the

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Vol. 19, No. 6 869 WATER CHEMISTRY, MICROSTRUCTURE EFFECT

s o i l , the degree o f p o l l u t i o n and i n d u s t r i a l wastes. I t i s t h e r e - f o r e w o r t h w h i l e c a r r y i n g out d e t a i l e d study on the e f f e c t of our n a t i o n a l waters on the p r o p e r t i e s o f b u i l d i n g m a t e r i a l s . Par t i o f t h i s work w i l l i n c l u d e a d e s c r i p t i o n o f the m i c r o s t r u c t u r e development of the cement pastes mixed w i t h the d i f f e r e n t waters and Par t 2 w i l l deal w i t h the v a r i a t i o n of the phys i ca l and mechanical p r o p e r t i e s of cement pastes and conc re te .

M a t e r i a l s I . Sea Water

The s a l i n e water was procured from the Red Sea at the Suez Canal r eg ion where s a l i n i t y i s known to be h ighe r than the Med i te r ranean . Samples from beaches a t Suez, Fayed, and I s m a i l i a were s u p p l i e d a t d i f f e r e n t t imes and ana lysed . The s u l f a t e , c h l o r i d e , hardness and pH of the waters were measured accord ing to the s tandard methods o f a n a l y s i s of waters and waste w a t e r ( 7 ) . The data presented in Table I show an a lmost cons tan t s u l f a t e ion c o n c e n t r a t i o n o f about 2500 ppm, a remarkab le i nc rease in the hardness o f water in a 2 -year p e r i o d ( f rom 3850 ppm in 1985 to 7640 in 1987) and a less s i g n i f i c a n t f l u c t u a t i o n in the c h l o r i d e ion c o n c e n t r a t i o n du r ing the same pe r i od w i t h an average va lue of about 27600 ppm. Sample No.1 was used f o r m ix ing cement pastes.

TABLE I Chemical A n a l y s i s o f S a l i n e Water Supp l ied from Suez Canal Region

Sample S i t e Supply pH S03 T o t a l Ca C1 s o l . No. Time Hardness s a l t s

ppm ppm ppm ppm ppm

I Cabanon 4.85 7 .6 2533 3683 580 31030 - - - 2 Canal Club 4.85 8 .5 2533 3850 - - - 23700 - - - 3 I s m a i l i a 4.87 8 .0 2500 7640 1200 27090 - - - 4 I s m a i l i a 7.87 7.9 2458 7600 1500 27390 25.7 5 Fayed 7.87 8.0 2500 7300 1300 27860 30.6 6 Cabanon 7.87 8 .0 2458 7800 I000 28320 40.5 7 Canal Club 7.87 8 .0 2491 7500 1400 27860 34.6

2. Ground Water Most o f the ground water samples analysed f o r the purpose o f

the p r o j e c t were found to be below the agg ress i ve l i m i t s p e c i f i e d f o r the conc re te a t t a c k . The f i r s t sample was taken from a con- s t r u c t i o n s i t e near the Pyramids from a depth o f 18 meters. Then

Chemical A n a l y s i s TABLE 2

of Ground Water Supp l ied from D i f f e r e n t S i t e s around Ca i r o

To ta l Sample S i t e Supply pH S03 Hardness Ca Cl

No. Time ppm ppm ppm ppm

I M a r i o u t i a 4.85 7 .8 431 307 - - - 315 2 Maadi 4.85 8 .6 900 452 232 685 3 Margh 4.87 7.9 450 500 340 170

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870 Vol. 19, No. 6 H.Y. Ghorab, et al.

a second bulk supp ly was ob ta i ned from ano ther c o n s t r u c t i o n s i t e

a long the r i v e r N i l e in southern C a i r o . The water was a t a depth o f around 5 meters which e x p l a i n s i t s r e l a t i v e l y h igh s a l i n i t y , rep resen ted in the s u l f a t e s ~ compared to the o the r water samples (Tab le 2) . A t h i r d bulk supply was taken from a v i l l a g e about 15 km n o r t h e a s t o f Ca i ro a t a depth o f 30 m. For the present s tudy, ground water No.2 was used f o r m ix ing cement pastes.

3. N i l e Water The samples s t u d i e d were procured from the N i l e r i v e r or i t s

branches near C a i r o . Some of the samples were s u p p l i e d tw ice from the same source a t d i f f e r e n t t imes and analysed f o r comparison. The r e s u l t s o b t a i n e d (Tab le 3) show t h a t the c h l o r i d e con ten t l i e s between 18 and 30 ppm and the s u l f a t e c o n c e n t r a t i o n v a r i e s between 21 and 83 ppm S03. Sample No . l was used f o r mix ing cement pastes and conc re te .

TABLE 3 Chemical A n a l y s i s o f the N i l e Water

To ta l Sample S i t e Supply pH S03 Hardness Ca C1

No, Time ppm ppm ppm ppm

1 Gamgara 6.85 8.6 56 75 35 28 2 Qanater 4.87 8.1 21 140 80 30 3 Gamgara 7.87 7.8 50 240 160 21 4 Mansoura 7.87 7.8 58 160 120 19 5 Banha 7.87 7.4 33 160 120 22 6 Shubra 7.87 7.9 41 160 120 18 7 Qanater 7.87 8.6 83 160 i00 26

4. Tap Water Table 4 g i ves a survey on the c o n c e n t r a t i o n o f tap water

w i t h i n two years t ime . TABLE 4

Chemical A n a l y s i s of D r i nk i ng Water

Sample Date pH S03 Cl No. ppm ppm

i 6.85 7.3 35 32 2 9.85 7.i 34 46 3 3.87 8.0 26 50 4 6.87 7.6 37 64 5 6.87 7.4 33 60 6 7.87 7 .5 22 60 7 7.87 8 .2 24 38 8 7.87 7.4 26 38 9 7.87 7 .9 30 35 i0 7.87 8.2 27 60

The r e g u l a r a n a l y s i s of tapwater shows a v a r i a b l e c o n c e n t r a t i o n o f the s u l f a t e and c h l o r i d e ions d u r i n g the pe r i od of study l y i n g f a r below the maximum p e r m i s s i b l e l i m i t f o r the use in concre te mixes.

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H y d r a t i o n Procedure

The e f f e c t o f water type on the behav iou r of neat cement pastes has been s t u d i e d by means of X- ray d i f f r a c t i o n a n a l y s i s us i ng a P h i l l i p s type 1390 d i f f r a c t o m e t e r w i t h Cu K - r a d i a t i o n and Ni f i l t e r . O r d i n a r y p o r t l a n d cement (OPC), EI -Karnak cement (EKC) manufactured by g r i n d i n g 25% s i l i c e o u s sand w i t h OPC c l i n k e r , and p o r t l a n d b l a s t f u r n a c e s lag cement (PBC) w i t h 35% s lag have been mixed w i t h the abovementioned types of water us ing a water cement r a t i o of 2. The h y d r a t i o n proceeded in w e l l s t op - pered p l a s t i c b o t t l e s f o r 2, I0 and 30 m inu tes , I hour , 1,7 and 28 days. For OPC samples the h y d r a t i o n was f o l l o w e d up to one yea r . The samples were shaken from t ime to t ime and a t the d e f i n i t e t ime i n t e r v a l the r e a c t i o n was stopped by i s o p r o p y l a l - c o h o l . The samples were f i l t e r e d o f f , d r i e d a t 50 degrees C e l s i u s f o r one day then ana lysed by means of X- ray d i f f r a c t i o n .

R e s u l t s and D i scuss i on

The h y d r a t i o n p roduc ts formed by m ix ing OPC w i t h tap wa te r , N i l e water or ground water f o r t ime up to 28 days are q u i t e s i m i l a r . R e p r e s e n t a t i v e samples are shown i n F i gu re I . The e t - t r i n g i t e phase appears a t a d - v a l u e of 9 .7 A and i s seen to e x i s t w i t h o u t a remarkable i n c r e a s e i n a l l samples up to 28 days. Th is o b s e r v a t i o n does no t n e c e s s a r i l y mean the presence of t h i s phase i n a smal l amount but m igh t be a t t r i b u t e d to i t s smal l p a r t i c l e s i z e and scann ing e l e c t r o n microscope s t u d i e s are needed f o r f u r - t h e r e x a m i n a t i o n .

No o t h e r h y d r a t i o n p roduc ts are to be de tec ted in the d i f - f r ac tog rams up to one day where the p o r t l a n d i t e phase s t a r t s to show up and i n c r e a s e s markedly f o r l onge r h y d r a t i o n p e r i o d . The appearance of p o r t l a n d i t e c r y s t a l s i s accompanied by a decrease i n the amount o f the anhydrous c l i n k e r phase ( a l i t e , b e l i t e , C3A and C4AF) which d i f f r a c t i o n l i n e s are c o l l e c t i v e l y found i n the m idd le of the d i f f r a c t o g r a m s , i . e . , between 3.02 and 2.b0 A. The c a r b o n a t i o n process i s observed i n the 3-day hydra ted sample where the monocarboaluminate hyd ra te i s de tec ted bes ide the c a l - c i t e . Both phases are found to i n c r e a s e w i t h t ime .

The h y d r a t i o n of OPC i n sea water causes a r a p i d p r e c i p i t a - t i o n of the gypsum phase wh ich appears a l r e a d y a f t e r two minutes from the r e a c t i o n s t a r t ( F i g u r e 2 ) . The gypsum phase i nc reases d u r i n g the f i r s t hour and the 9.7 A l i n e of e t t r i n g i t e i s w e l l r e c o g n i s e d . Gypsum does no t remain up to 28 days but i n s t ead the c a l c i u m c a r b o - , s u l f o a l u m i n a t e h y d r a t e form.

The amount o f h y d r a t i o n p roduc ts formed d u r i n g the h y d r a t i o n process o f EKC w i t h tap wa te r , ground water and N i l e water exceeds t h a t o f the OPC hydra ted under o t h e r w i s e s i m i l a r c o n d i - t i o n s . Th i s i s seen from the o b v i o u s l y h i g h e r i n t e n s i t i e s of the p o r t l a n d i t e and e t t r i n g i t e phases a f t e r one day, shown i n F i g . 3 w i t h the N i l e water as an example. The gypsum formed d u r i n g the h y d r a t i o n process i n sea water i s r a p i d l y consumed in f avou r of the s u l f a t e - b e a r i n g monophase f o r m a t i o n ( d - v a l u e a t 8 .2 A) . The

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872 Vol. 19, No. 6 H.Y. Ghorab, et al.

Id

2 E 10

20 15 10 5 ~--g

Fig . I . X-Ray D i T f r a c t i o n of OPC Paste with Tap Water

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Vol. I9, No. 6 873 WATER CHEMISTRY, MICROSTRUCTURE EFFECT

!L 28

20 15 10 5 Q

F i g . 2. X-Ray D i f f r a c t i o n of OPC Paste w i th Sea Water

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874 VoI. 19, No. 6 H.Y. Ghorab, el: al.

I !H C- J 28d ~V~ CH Mc E

I Ctinker

F i g . 3. X-Ray D i f f r a c t i o n o f EKC Paste w i t h N i l e Water

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Vol. 19, No. 6 875 WATER CHEMISTRY, MICROSTRUCTURE EFFECT

q u a l i t a t i v e behav iour of the phases i s g e n e r a l l y s i m i l a r to t ha t of the OPC h y d r a t i o n .

The h y d r a t i o n of the PBC w i t h tap water , ground water and N i l e water d id not d i f f e r much from one another . The p r e c i p i t a t e d

cc I H 28d

20 15 10 5 ~--@

F ig . 4. X-Ray D i f f r a c t i o n of PBC Paste w i t h N i l e Water

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876 Vol. 19, No. 6 H.Y. Ghorab, et al.

CH Cc C H

v ~ 20 15 10 5 -~ g

F i g . 5. X-Ray D i f f r a c t i o n of PBC Paste w i t h Sea Water

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Vol. 19, No. 6 877 WATER CHEMISTRY, MICROSTRUCTURE EFFECT

hydra ted l ime appears i n the f i r s t day as i n the o t h e r two ce- ments. The amount o f p o r t l a n d i t e i n c r e a s e s w i t h t ime and the f o r - mat ion of the c r y s t a l l i n e monocarboaluminate hyd ra te i s not predominant ( F i g . 4 ) . However the amount o f p o r t l a n d i t e formed in the presence of sea water decreases w i t h t ime and the s u l f a t e -

• ~ W ~ 4 to

20 15 10

OUJ

O0 A

5~-0

F i g . 6. X-Ray D i f f r a c t i o n o f OPC Paste w i t h D i f f e r e n t Types of Water a t the Age of One Year

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878 Vol. 19, No. 6 H.Y. Ghorab, et al.

bear ing monophase ( d - v a l u e 8.2 A) becomes the predominant product a f t e r 28 days (F i gu re 5) .

The X- ray d i f f r a c t i o n p a t t e r n s of r e p r e s e n t a t i v e samples of the OPC pastes hydra ted f o r one year are shown i n F i g u r e 6. The p roduc ts formed in the presence of the f o u r water types are s i m i l a r except f o r an excess amount of the e t t r i n g i t e over the monophase in the presence of sea wa te r . The phases formed are e t - t r i n g i t e ( d - v a l u e 9.7 A) , s u l f a t e - b e a r i n g monophases ( d - v a l u e 8.2 A) and monocarboaluminate hyd ra te ( d - v a l u e 7.6 A) . Some un- a v o i d a b l e c a r b o n a t i o n i s de tec ted a t a d - v a l u e of 3.03 A and the ca l c ium h y d r o x i d e phase i s e a s i l y de tec ted a t 4 .9 and 2.62 A.

Conc lus i on

I . Gypsum p r e c i p i t a t e s o n l y d u r i n g the h y d r a t i o n of the cements w i t h sea water but d i sappears i n f a v o u r of the ca l c i um s u l f a t e - bear ing monophases. 2. The p r e c i p i t a t i o n of the p o r t l a n d i t e takes p lace in the f i r s t h y d r a t i o n day. I t i n c reases w i t h t ime w i t h the appearance of a s u l f a t e - f r e e monophase i n the presence of tap wa te r , N i l e water and ground water but decreases w i t h the f o r m a t i o n of s u l f a t e - bear ing monophase i n the presence of sea wa te r . Th i s i s most ob- v i o u s i n PBC. 3. The q u a l i t y and q u a n t i t y of phases formed a f t e r one year i n the hydra ted OPC pastes are u n a f f e c t e d by the water t ype .

References

i . R.C.Smith and D . J . C a l v e r t , J. Pet . Techn. , 27, 759 (1975) . 2. M.Kawamura and Y.Yamada, Semento G i j u t s u Nempo, 28, 180 (1974) 3. F.M.Lea, the Chemis t ry of Cement and Concre te , Edward A rno ld ,

L t d . , London (1956) . 4. R .E I -She ikh ,H.EL-D idamony and M.Haggag, T IZ , I07 , 73b (1983). 5. M.Regourd, Pub. SP-&5, Amer. Conc. I n s t . , 63 (1980) . b. V .M .MA lho t ra , G.G.Gare t te and T.W.Bremner, CANMET Repor t ,

80-18E, 27 pp . , 1980. 7. Standard Methods f o r the Examina t ion of Water and Waste Water,

American P u b l i c Hea l t h A s s o c i a t i o n , 439 (1980) . 8. H.Ghorab, M . S . H i l a l and S . A b o u l - F e t o u h , Proc. Symp. Q u a l i t y

and Performance of Cement and Concrete i n the Arab World, Baghdad, I r a k , 187, 2-5 Nov.1987.