Deterioration of Sandstone in the Historical and Contemporary Sea Walls upon the Impact of the Natural and Man-Made Hazards
Abstract
:1. Introduction
1.1. Historical Background of the Place
1.2. Materials and Construction Methods Used in the Panorama Sea Walls
2. Defects Appeared in the Panorama Sea Walls
- -
- Group 1—Loss of stone material:
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- Group 2—Coloration/Deposits
3. Experimental and Results
- Was it realistic to predict kurkar stone durability trends before its implementation in the Panorama Sea Wall?
- What factors have led to the quick deterioration of kurkar stone siding in the contemporary Panorama Sea Wall, although the kurkar stones in Acre’s historic sea wall were less deteriorated?
3.1. Mineral Composition
3.2. Physical Properties and Strength
- S > 0.85—susceptible.
- 0.75 < S < 0.80—moderate resistant.
- S < 0.75—frost resistant.
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- The decreased compressive strength and modulus of rupture, i.e., a drop of 16 to 23% and 18 to 35%, respectively.
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- The capillary absorption rise: 4.9 to 7.6 times as much as of the original unweathered stone.
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- The total absorption has dramatically risen due to weathering, and it was 1.5 times more than in the original unweathered stone.
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- A sharp decline of the initial evaporation capacity was observed: about twice as less as in the unweathered stone.
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- An increase in the saturation (Hirschwald’s) coefficient of weathered stones is more than twice as high as observed in the unweathered samples.
3.3. Soundness
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- Perpendicular to rift plane—from 3291 to 4956 g per m2 per h½ or 2.9 to 4.4 % (w. %).
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- Parallel to rift plane—from 3989 to 4227 g per m2 per h½ or 3.5 to 3.8% (w. %).
4. Discussion
- (a)
- Sulphuric and nitric acids, which are supplied by acid precipitation because of air pollution, take over from carbonic acid in weathering reactions of albite, which induced a decrease in the atmospheric/soil CO2 consumption by weathering [32]. The high air pollution in the urban environment causes dissolving CO2 in water and carbonic acid formation afterward. This process promotes the mineral weathering of albite feldspar in kurkar sandstone and results in albite kaolinization [32,33,34]:
- (b)
- Kurkar sandstones in the Panorama Sea Walls have always been exposed to the non-stop dry–wet cycles in acidic and alkaline environments with high levels of air pollution (acidic pH ca. 4.0 (estimated) and seawater breeze (alkaline pH ca. 8.5–9.0), respectively. The dissolution reactions of albite and calcite minerals that form cement in sandstone are too spontaneous in an acidic environment. In an alkaline solution, the dissolution reaction of quartz in sandstone is spontaneous [25,28]. The dissolution of the large amounts of sandstone cement explains kurkar crumbling (see Figure 5) and a sharp decrease in the mechanical properties of naturally weathered kurkar (see Table 2). A sharp rise in capillary absorption could be partially attributed to quartz (aggregate) dissolution leading to the high sandstone porosity, see Figure 7. A dissolution of silicon and a release of iron (II) ions from biotite subjected to the solutions with the low and near neutral (alkali) pH is found to occur within the first ten months of exposure [32,34]. The oxidation of iron (II) to iron (III) in Panorama Sea Walls’ sandstone might be a rapid process given the seawater chlorides absorbed by kurkar. Furthermore, the rusty coloration of kurkar, see Figure 10, has resulted from these redox reactions of iron phases released by biotite because of its degradation.
- (c)
- The walls were cast in-situ against sandstone veneer siding. Thus, one can conclude with confidence that kurkar stone has been, for at least 28 days, in direct contact with fresh and hardening cement-based matrix, which means that kurkar absorbed high pH alkali solutions from concrete. It is common knowledge that the pH of fresh and hardening concrete is ca.12 to 13, and alkalis in it are Ca2+ (major alkali) and Na+& K+ (minor alkalis).). Furthermore, salt-containing seawater breeze and acid air pollution in Acre Bay have promoted the formation of significant efflorescence at kurkar face surface, see Figure 7 and Figure 9 (The chemical composition of such efflorescence might be variable and consists of the following salts: halite, NaCl, thenardite, Na2SO4, mirabilite, Na2SO4·10H2O, thermonatrite, Na2CO3·H2O, gypsum anhydrite, CaSO4 and gypsum, CaSO4·2H2O, depending on (a) seawater moisture content in kurkar sandstone, (b) concentration of alkalis absorbed by sandstone from fresh and hardening mortar/concrete and (c) levels of the local air pollutions [28,29,30,31,32,33,34,35,36,37,38,39,40,41,42].
- Water absorption and Hirshwald’s coefficient have been substantially increased;
- Water evaporation and mechanical strength have been considerably decreased.
Impact of Construction Technology on Durability of Kurkar Sandstones in the Historic Sea Walls Versus the Panorama Sea Walls in Acre
- The ashlar kurkar blocks, ca. 0.3–0.6 m long, thick, and wide by size, were used in the Historic Walls’ stonework in Acre. In these Walls, the bed joints were made of air lime mortar, [41], see Figure 15. Air lime mortar covered ca. 15% of each kurkar block’s total surface, and the rest of the body has been left breathable and useful for the evaporation of moisture from the historic sea walls.
5. Conclusions
Funding
Institutional Review Board Statement
Informed Consent Statement
Data Availability Statement
Conflicts of Interest
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Property | Minimal Value | Maximal Value | Average | Standard Deviation | Requirements for Average Value [11] | Test Method |
---|---|---|---|---|---|---|
Bulk density, kg/m³ | 1850 | 2120 | 2010 | 106 | ≥2500 | ASTM C97-18 [12] |
Total water absorption, mass % | 3.4 | 8.64 | 6.1 | 1.6 | <2 | ASTM C97-18 [12] |
Capillary water absorption, g per m2 per hour | 2400 | 2680 | 2600 | 55 | ≤500 | EN 1925–1999 [13] |
Modulus of rupture, MPa | 2.7 | 8.6 | 4.9 | 1.7 | > 3 | ASTM C99-2000 [14] |
Property | Unweathered Stone | Weathered Stone (Cored from the Wall) | ||||||
---|---|---|---|---|---|---|---|---|
Minimal Value | Maximal Value | Average | Standard Deviation | Minimal Value | Maximal Value | Average | Standard Deviation | |
‘Capillary absorption coefficient, g per m2 per hour½ | 1747 | 25,398 | 13,569 | 8924 | ||||
| 1601 | 1907 | 1777 | 158 | ||||
| 2073 | 3176 | 2765 | 603 | ||||
Total water absorption, W, mass % | 3.3 | 10.4 | 4.8 | n/a | 3.7 | 13.0 | 7.3 | n/a |
Saturation (Hirschwald’s) coefficient [22] | 0.76 | 0.80 | 0.78 | n/a | ||||
| 0.3 | 0.5 | 0.35 | n/a | ||||
| 0.4 | 0.6 | 0.52 | n/a | ||||
Water evaporation capacity, w. %, after | ||||||||
| 68% | 30% | ||||||
| 90% | 83% | ||||||
| n/a | n/a | 100% | n/a | n/a | n/a | 91% | n/a |
Compressive strength, MPa | ||||||||
| 6.3 | 34.4 | 14.0 | 8.8 | 6.8 | 25.6 | 11.7 | 8.6 |
| 3.7 | 12.5 | 6.6 | 3.0 | 2.1 | 10.1 | 5.1 | 2.2 |
Modulus of rupture, MPa | ||||||||
| 4.2 | 8.8 | 6.2 | 1.7 | 2.8 | 4.0 | 4.0 | 1.4 |
| 3.3 | 6.0 | 4.9 | 1.1 | n/a | n/a | n/a | n/a |
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Wasserman, R. Deterioration of Sandstone in the Historical and Contemporary Sea Walls upon the Impact of the Natural and Man-Made Hazards. Appl. Sci. 2021, 11, 6892. https://doi.org/10.3390/app11156892
Wasserman R. Deterioration of Sandstone in the Historical and Contemporary Sea Walls upon the Impact of the Natural and Man-Made Hazards. Applied Sciences. 2021; 11(15):6892. https://doi.org/10.3390/app11156892
Chicago/Turabian StyleWasserman, Rina (Irena). 2021. "Deterioration of Sandstone in the Historical and Contemporary Sea Walls upon the Impact of the Natural and Man-Made Hazards" Applied Sciences 11, no. 15: 6892. https://doi.org/10.3390/app11156892
APA StyleWasserman, R. (2021). Deterioration of Sandstone in the Historical and Contemporary Sea Walls upon the Impact of the Natural and Man-Made Hazards. Applied Sciences, 11(15), 6892. https://doi.org/10.3390/app11156892