saline solution properties - upv/ehu · studied saits the na2s04-h20 system includes two stable...

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MACLA 6 XXVI REUNiÓN (SEM) / XX REUNiÓ N (SEA) - 2006 SALT WEATHERING BY SULFATES: INFLUENCE OF SALINE SOLUTION PROPERTIES E. Rurz-AGUDO y C. RODRÍGUEZ-NAVARRO Dept. Mineralogía y Petrología, Universidad de Granada, Fuentenueva s/n, 18002 Granada, Spain. INTROOUCTION The crystallization of soluble salts in porous materials is one of the major causes rock decay in nature (e.g., arid and desert regions, coastal are as, Antarctica -Evans, 1970; Winkler and Singer, 1972) and weathering of stone buildings and other engineering structures (Winkler, 1994; Goudie et al. 1997; Rodriguez-Navarro and Doehne, 1999). The growth of a crystal in a confined space (pore) can exert a pressure sufficient to exceed the rupture modulus of most ornamen- tal materials, including stone, mortars and bricks, causing their breakage. It is therefore important to know the mechanisms of damage and the parameters controlling the process of salt weathering as a first step to design methods to mitigate this problem in the fields of civil engineering and cultural heritage conservation. Here we have studied differences in crystallization behavior of sodium and magnesium sulfates. These two salts are extensively found in both new cement structures and porous building stones. Both are extremely damaging and show completely different crystallization patterns; however, their damage mechanism has not yet been clarified. Our study reveals soe keys parameters which control salt damage of porous stone, such as where crystallization occurs and in what kind of pores in the case of each salt are ultimately determined by pore size distribution of stone and salt solution properties. These results may help elucidate why these salts are so damaging, which is critical to designing possible solutions to reduce damage caused by such sulfates. MATERIALS ANO METHODS Studied saIts The Na 2 S04-H 2 0 system includes two stable phases: thenardite (Na 2 S04), the anhydrous phase that precipitates directly from solution at temperatures aboye 32.4°C, and mirabilite (Na 2 S04·1 0H 2 0), the stable phase below this temperature. Mirabilite dehydrates to thenardite at RH below 71 % (20 ºC). Sodium sulfate heptahydrate (Na 2 S04·7H 2 0) has been described as precipitating at temperatures below the mirabilitej thenardite transition point. However, this phase is metastable and has not been clearly identified in nature. On the other hand, the only naturally occurring members of the MgS04'nH 2 0 series on Earth are epsomite (MgS04·7H 2 0, 51 wt% water), hexahydrite (MgS04·6H 2 0, 47 wt% water) and kieserite (MgS04·H 2 0, 13 wt% water). Epsomite transforms readily to hexahydrite by loss of ex- tra-polyhedral water; this transition is reversible and occurs at 50-55% relative humidity (RH) at 298 K and at lower temperatures as the activity of water diminishes (Vaniman et al., 2004). Both magnesium and sodium sulfates are used for stone accelerated decay testing because their crystallization is highly damaging (ASTM 1997; Rodriguez-Navarro and Doehne, 1999). Stone characterization The damaging effects of salt crystallization within a na- tural porous medium were studied using a biomicritic limestone (calcarenite). The calcarenite was quarried in the Santa Pudia area (15 km SW from Granada). It is buff colored, quite porous and easy to quarry and carve. These characteristics led to its extensive use in the Andalusian's architectural and sculptural heritage. It has well-known salt weathering problems. The calcarenite overall porosity, determined by mercury intrusion porosimetry (MIP), is 32.2 %, with a mean pore radius of 13.5 flm. Calcarenite pore size distribution graphs (Fig. 3) show abundant macropores, with a mean pore radius of ca. 30 flm. Sma ller pores are also detected with secondary : : 1 - · 0 0018 ---------------- 0 0016 J b 0. 80 · 0.70 "!O.60 J : : j 030 0,20 0.10 0.00 - - 0.00 0.20 0.40 0. 0.80 1.00 PIPo 0 0014 I 0. 001 2 J J > 0.001 0 0,0008 0, 0006 E 0.0004 00002 0.0000 10 100 Radlus (Al 1000 10000 MACLA Figure 1: N 2 sorption isotherms (a) and BJH pare size distribution (b) of Santa Pudia's limes tone 6 Página 43 1

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Page 1: SALINE SOLUTION PROPERTIES - UPV/EHU · Studied saIts The Na2S04-H20 system includes two stable phases: thenardite (Na2S04), the anhydrous phase that precipitates directly from solution

MACLA 6 XXVI REUN iÓN (SEM ) / XX REUN iÓN (SEA) - 2006

SALT WEATHERING BY SULFATES: INFLUENCE OF SALINE SOLUTION PROPERTIES

E. Rurz-AGUDO y C. RODRÍGUEZ-NAVARRO

Dept. Mineralogía y Petrología, Universidad de Granada, Fuentenueva s/n, 18002 Granada, Spain.

INTROOUCTION

The crystallization of soluble salts in porous materials is one of the major causes rock decay in nature (e.g., arid and desert regions, coastal are as, Antarctica -Evans, 1970; Winkler and Singer, 1972) and weathering of stone buildings and other engineering structures (Winkler, 1994; Goudie et al. 1997; Rodriguez-Navarro and Doehne, 1999) . The growth of a crystal in a confined space (pore) can exert a pressure sufficient to exceed the rupture modulus of most ornamen­tal materials, including stone, mortars and bricks, causing their breakage. It is therefore important to know the mechanisms of damage and the parameters controlling the process of salt weathering as a first step to design methods to mitigate this problem in the fields of civil engineering and cultural heritage conservation . Here we have studied differences in crystallization behavior of sodium and magnesium sulfates. These two salts are extensively found in both new cement structures and porous building stones. Both are extremely damaging and show completely different crystallization patterns; however, their damage mechanism has not yet been clarified. Our study reveals sorne keys parameters which control salt damage of porous stone, such as where crystallization occurs and in what kind of pores in the case of each salt are ultimately determined by pore size distribution of stone and salt solution properties. These results may help elucidate why these salts are so damaging, which is critical to designing possible solutions to reduce damage caused by such sulfates .

MATERIALS ANO METHODS

Studied saIts

The Na2S04-H20 system includes two stable phases : the n a r d i te ( N a2S04) , t h e anhy d r o u s p h a s e t h a t

precipitates directly from solution a t temperatures aboye 32.4°C, and mirabilite (Na2S04· 10H20), the stable phase b e low this t e m p e r a tur e . Mirabi l i te dehydrates to thenardite at RH below 71 % (20 ºC) . Sodium sulfate heptahydrate (Na2S04 · 7H20) has been described as pre cipitating at temperatures below the mirabilitej thenardite transition point . However, this phase is metastable and has not been clearly identified in nature . On the other hand, the only naturally occurring members of the MgS04 ' n H20 s e r i e s on E a r th a r e e p s omite (MgS04·7H20, 51 wt% water), hexahydrite (MgS04·6H20, 47 wt% water) and kieserite (MgS04·H20, 13 wt% water) . Epsomite transforms readily to hexahydrite by loss of ex­tra-polyhedral water; this transition is reversible and occurs at 50-55% relative humidity (RH) at 298 K and at lower temperatures as the activity of water diminishes (Vaniman et a l . , 2004) . Both magnesium and sodium sulfates are used for stone accelerated decay testing because their crystallization is highly damaging (ASTM 1997; Rodriguez-Navarro and Doehne, 1999) .

Stone characterization

The damaging effects of salt crystallization within a na­tural porous medium were studied using a biomicritic limestone (calcarenite ) . The calcarenite was quarried in the Santa Pudia area (15 km SW from Granada) . It is buff colored, quite porous and easy to quarry and carve . These characteristics led to its extensive use in the Andalusian's architectural and sculptural heritage. It has well-known s a l t w e athering p r o b l e m s . The c a l c arenite overal l porosity, determined by mercury intrusion porosimetry (MIP), is 32 .2 %, with a mean pore radius of 13 .5 flm . Calcarenite pore size distribution graphs (Fig. 3) show abundant macropores, with a mean pore radius of ca. 30 flm . Smaller pores are also detected with secondary : :1-· 0 00 1 8 ,-------------------,

0 0016 J b 0 . 80 · 0.70

"!!!O.60 ¡¡

J: : j 0 30 0,20 0.10 0.00 "'�'-.--'--

0.00 0.20 0.40 0.00 0.80 1.00 PIPo

"; 0 0014 � I 0.001 2 JJ > 0.0010 I! � 0,0008 ;¡; � 0,0006 E � 0.0004 .5 0 0002

0.0000 +--_......,..._�:;:;.-_ 1 0 1 00

Radlus (Al 1 000 10000

MACLA

Figure 1 : N2 sorption isotherms (a ) and BJH p a re s ize d is t r i b u t i on (b ) of San ta Pudia 's limes tone

6 Página 43 1

Page 2: SALINE SOLUTION PROPERTIES - UPV/EHU · Studied saIts The Na2S04-H20 system includes two stable phases: thenardite (Na2S04), the anhydrous phase that precipitates directly from solution

MACLA 6 XXVI REUN iÓN (SEM) / XX REUN iÓN (SEA) - 2006

W(t)max' % V %/hI12 des, Csuc, g/cm'h' /2

Limestone 19. 14 14.70 23. 1 7 6.39 3 .71 12 .9 2.75 W(t)max: maximum water content (saturation); W(t)abs: maximum water content (absorption); ; 1m: microporosity index; Vabs: absarptioll velocity; Vdes: desol'ption velocity; Vcap: capillary suctíon velocity;; Csucc: capíllary suctían coefficient

Table 1 : Hydric characteristics of Santa Pudia 's Limestone (from Rodríguez-Navarro, 1 994)

maxima at ca , 0 . 1 flm. The calcarenite shows a small specific surface area (0.815 m2/g, according to the BET method) , The nitro gen absorption isotherm (Fig, l a) is of type I1I, typical of non-microporous solids. The BJH plot (Fig, lb) shows the presence of a significant amount of meso and macropores (pore radius > 50 nm) . Hydric properties are summarized in Table 1 (Rodriguez-Nava­rro, 1994) ,

Macroscale salt crystallization experiments

S a t u r a t e d s a l t s o lut i ons w e r e p r e p a r e d f r o m crysta l l ine s o l i d (Panre a c, analyt ica l g r a d e ) u s i n g deionized water, filtered and heated t o eliminate any undissolved salt crystals, Salt crystallization tests were carried out in a controlled environment (20±2ºC, and 45±5% relative humidity ) . The s olutions were let to flow-through, evaporate and crystallize in the porous stone (Fig. 2). See Rodriguez-Navarro et al . (2002) for d e t a i l s on the l a b o r a tory s e t -up . The s o lu t i o n evaporation rate was measured b y continuous weighing of the stone-solution-beaker system, Salt crystals grown within the stone, as well as on its surface (efflorescence) were collected after crystallization experiments and examined by p o w d e r X-ray diffract ion (XRD) and environmental scanning microscopy (ESEM) with no prior treatment (i . e " no grinding) in order to infer their growth morphologr-

RESULTS AND DISCUSSION

Porosity and pore size distribution are key factor s controlling the uptake and transport of liquid within a stone (Rodriguez-Navarro and Doehne, 1999) , Stones such as Santa Pudia's limes tone with a high proportion of mesopores connected to large pores are very susceptible to salt weathering. These mesopores result in larger surface a r e a for evaporat ion and s lower s o lut ion t ranspo rt, thu s increas ing the chances that high supersaturation ratios will be reached below the stone surface (subflorescence growth) , In stones with larger pores, capillary rise is limited, surface are a is lower, and s o lutions read i ly reach the s tone surface, without a chieving a high supersaturation, thus resulting in efflorescence growth,

Hydric properties (Table 1) show that the calcarenite rapidly absorbs water, but dries slow. Thus, salt solutions will be taken up fast, but will remain within the stone pore system for enough time to precipitate as harmful subflorescence , Such behavior contributes to the overall susceptibility of this stone towards salt weathering. Crystallization of both Na sulfate and Mg sulfate reduce the stone porosity (29 ,5 and 24.2 %, respectively) and mean pore radius (3 . 1 and 6 . 4 flm, respectively) . Na sulfate induces the deposition of crystals within the bigger pores of the stone (Fig. 3a), close to the surface, forming thin stone surface layers that lift up successively (Fig. 4b) . ESEM analysis of salt crystals grown in stone slabs show direct precipitation of thenardite with bow-tie

MACLA 6 Página 432

0.18 0.16

� 0.14 ..J .§. 0.12 .. § 0.10 � 0.08 11: Q 0.06 "" .3 0.04

0.02 0.00

1000

0.18 0.16

� 0.14 ..J .§. 0.12 .. § 0.10 � 0.08 � 0.06 "" j 0.04

0.02 0.00

1 000

imestone b (3x3x2:Scm) s soIl.Itlon

(3OO ml)

2SO.004 g

Figure 2 : L a b o r a t o ry s e t - u p for crystallization experiments

a

1 00

b

100

Fresh sample (calcarentte)

_ Pores fi l led with Na2S04

10 1 0.1 Radius (f'ml

Fresh sample (calearenite)

10 1 O� Radius (f'm)

0.01 0.001

_ Pores fi l led with MgS04

0.01 0.001

Figure 3: MIP pare size dis tribution of limes tone befare and after crys tallization of Na sulfate (a) and Mg sulfate (b)

morphology (Fig. 5a) . Note that if mirabilite would have been precipitated first, and subsequently dehydrated, a porous crystal retaining mirabilite bulk shape would have formed. The observed morphology of thenardite is typical of crystallization at a high supersaturation (Sunawaga, 1 9 8 1 ) . The crystals thus generate high crystallization pressure and cause significant damage. Heterogeneous nucleation of Na2S04 over cal cite minerals in a limestone

Page 3: SALINE SOLUTION PROPERTIES - UPV/EHU · Studied saIts The Na2S04-H20 system includes two stable phases: thenardite (Na2S04), the anhydrous phase that precipitates directly from solution

MACLA

Figure 4 : S u lfa te damage in l imes tane s l abs : a) befare crystallizatian tests; b) after sadium sulfate crys tallizatian and e) after magnesium sulfate crystallizatian.

pore may induce thenardite precipitation and growth at temperatures below 32.4 ºC (Rodriguez-Navarro and Doehne, 2000). In contrast, Mg sulfate shows a decay mechanism b a s e d on c r a c k p r o p a g a t i o n ( F i g . 4 c ) . Epsomite precipitates deep into. the limes tone, filling large and small pores (Fig. 3b), with crystals displaying near equilibrium forms (Fig. 5b) . This was also observed by Rodriguez-Navarro and Doehne (1999) in the case of halite formed within limestone.

These results disagree with the generally accepted Wellman and Wilson (1 965) theory for salt crystallization.

Figure 5: ESEM micragraphs af sulfates grawing in limestane pares: a) Na sulfate and b) Mg sulfate.

6 XXVI REUNiÓN (SEM) / XX R E U N iÓN (SEA) - 2006

Saturated Concentration

Density Surface

Viscosity Vapor

solution ( g anhyd.1100

(g/cm') Tension

(eP) Pressure

gH,o) (mNfm) (kPa)

Na,SO. 19.4 1 .15 75.45 1 .834 2.175 MgSO. 33.5 1 .29 77.35 7.270 2.781

Tab l e 2 : Phys i ca l p raper t ies af s a l t s a l u t i an s used in crystallizatian experiments (20ºC).

According to this theory, the crystal/saturated solution surface free energy is higher in smaller pores than in coarser ones because of volume constraints. Thus salt crystallization is thermodynamically not favorable in small pores. However, it has to be taken into account that ionic transport in porous materials is a competition between salt advection to the evaporation front, and ion diffusion (Pel, 2002) . Drying rate is the key parameter that controls the prevalen ce of one mechanism or the other. If the drying is slow, diffusion controls the process (Rijniers, 2004) . As water evaporates in large p ores, ions are transported to small pores where the concentration is lower. Finally, crystallization takes place in both large and small pores at a very high supersaturation, thus leading to important damage . This is the case of Mg sulfate. If the drying is very fast, salt is transported by advectíon to the p o s i t ion where e v a p o r at ion t a k e s p l a c e and sa l t s precipitate, that is to say, in large pores. This behavior was observed in the case of Na sulfate.

U l t i m a t e ly, the p h y s i c a l p r o p e r t i e s of a s a l ine solution ( i . e . , viscosity, density, surface tension and va­por pressure) will control the dynamics of solutíon flow and evaporation within the porous network of the s t o n e ( s i n c e environmenta l c o n d i t i o n s w e r e kept constant in our tests), and therefore the dynamics o f precipitation and salt growth and the resulting damage to porous substrate. Flow is governed by Poseuille's law, where the driving force is capi l lary p r e ssure (Lewin, 1 982) . The differential flow behavior of the two s aline solutions is mainly due to the differences in viscosity (Table 2). Due to its higher viscosity, capillary flow i s s lower in the case of saturated magnesium sulfate solution (compared with that of sodium sulfate s o lution at the RH and T of the experiment) . As a c o n s e qu e n c e , e v a p o r a t i o n o c c u r s f a s t e r than the replenishment of the solution by capil lary nligration from the inside of the stone, and precipitation takes p l a c e u n d e r the s tone suda c e . The drying-out o f solution within a pore opening a t the surface occurs by diffusion of water vapor through a layer of the porous solid, and is governed by Fick's law. Once the solution

80 70 _ SODIUM SULFATE

-s- MAGNESIUM SULFATE � 60 E! � 50 o

...J 40 :l: .!al 30 <V :s: 20

1 0

20 40 60 80 1 00 t (h)

1 20 1 40 1 60

Figure 6: Evaparatian rate af sadium sulfate and magnesium sulfate saline salu tians fram limes tone slab.

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MACLA 6 XXVI REUN iÓN (SEM) / XX REUN iÓN (SEA) - 2006

reaches the evaporation front it would be expected that the e v a p o r at ion r a t e wi l l be fas t e r in the c a s e o f magnesium sulfate, as its vapor pressure i s higher (the e v a p o r a t i o n r a t e incre a s e s wi th vap o r p r e s s u r e ) . However, due to the fact that the evaporation front is p laced inner in the stone ( compared with s o dium sulfate) the rate of water vapor diffusion and, finally, the effective evaporation rate, would be much lower (Fig. 6) .

CONCLUSIONS

Both Na and Mg sulfate are extremely damaging salts, as has been observed in field and laboratory tests . While the mechanism of salt weathering by Na sulfate consists in the detaching of successive stone layers, Mg sulfate in­duces crack formation and propagation within the bulk stone . Differential damage created by Na sulfate and Mg sulfate is mainly due to differences in their crystallization pattern since we kept constant the environment variables (RH and T) and the porous support (Santa Pudia 's limestone) . The physical properties of the salt solution, i .e . density, surface tension, and, in particular, viscosity, have a critical effect on the dynamics of solution flow and evaporation within the stone, and therefore, on where crystallization occurs and in what kind of pores, as well as on the resulting damage to porous host materials. High flow rates lead to crystallization inside the stone in coarse pores. As a result of low flow rates within the porous network, crystallization takes place inside the stone in both small and big pores. Crystallization on stone surface as efflorescence would avoid/minimize stone damage due to salt crystallization. This can be achieved by acting not only on the crystallization process ( i .e . , increasing induct ion t i m e s by the a d di t ion of crystal l iza t ion inhibitors), but a l so in the solution transport process within the stone (i .e . , high flow rates), as they both play a crucial role in salt damage. The use of compounds (such as surfactants) that influence salt crystallization pattern by m o d ifying t ranspo r t/fl ow p r o p e r t i e s of s a l ine solutions inside porous materials may reduce salt damage in such building materials . This proposed treatment could enhance the effect of other methods that act mainly

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modifying the crystallization process (i .e . , crystallization inhibitors) .

ACKNOWLEDGEMENT

This work has been financial ly supported by the European Commission VIth Framework Program, under Contract no . SSP 1 -CT-2003-5 0 1 5 7 1 , and the research group NRM-1 79 (Junta de Andalucía, Spain) .

REFERENCES

ASTM C 88-90 (1997) ASTM Annual Book of Standards, 4 .2, 37- 42.

Evans, 1 . S. ( 1970) Rev. Geomorphologie Dynamique, 19, 153-1 77.

Goudie, A. S., Viles, H.A. ; Parker, A. G . J . Arid Environm. 1997, 37, 581-598

Lewin, S .Z . ( 1 982) In: « Conservation of Historic Stone Buildings and Monuments » , N . S . Baer, ed. National Academy Press, 120-162.

Pel, L . (2002) . Appl. Phys. Lett . , 81 ( 15), 2893-2895 . Rijn ie r s , L . ( 2 0 0 4 ) PhD d i s s e r t a t ion, Te chniche

Universiteit Eindhoven, 112 pp. R o d r iguez-Navarro , C. ( 1 9 9 4 ) PhD d i s s e r t a tion,

University of Granada, 412 pp. Rodriguez-Navarro, C. and Doehne, E. ( 1 999 ) E arth

Surface Processes Landforms, 24, 191-209. Rodriguez-Navarro, C . and Doehne, E . (2000) Cement

Concrete Res., 30, 1527-1534. Rodriguez-Navarro, c.; Linares-Fernandez, L.; Doehne,

E. and Sebastian-Pardo, E. (2002) J. Cryst. Growth, 243, 503-516 .

Sunagawa, I . ( 1981 ) Bull . Mineralogy, 104 ,81-87. Vaniman, D.T. ; Bish, D . L . ; Chipera, S . J . ; Fialips, c . I . ;

William Carey, J . ; Feldman, W.c . (2004) Nature, 431, 663-665 .

Wellman, H . W. and Wilson, A .T. ( 1 965) . Nature, 205, 1097-1098.

Winkler, E . M.; Singer, P . C . (1972) Geol . Soc o Am. Bull., 83(1 1 ), 3509-13 .

Winkler, E .M. ( 1994) Stone in Architecture, Properties and Durability. Springer-Verlag, Berlin, 313 pp.