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Article

Water-to-Cement Ratio of Magnesium Oxychloride Cement Foam Concrete with Caustic Dolomite Powder

1
Key Laboratory of Comprehensive and Highly Efficient Utilization of Salt Lake Resources, Qinghai Institute of Salt Lakes, Chinese Academy of Sciences, Xining 810008, China
2
Key Laboratory of Salt Lake Resources Chemistry of Qinghai Province, Xining 810008, China
3
Qinghai Building and Materials Research Co., Ltd., Xining 810008, China
4
The Key Lab of Plateau Building and Eco-Community, Xining 810008, China
*
Authors to whom correspondence should be addressed.
Sustainability 2021, 13(5), 2429; https://doi.org/10.3390/su13052429
Submission received: 27 January 2021 / Revised: 19 February 2021 / Accepted: 19 February 2021 / Published: 24 February 2021
(This article belongs to the Special Issue Sustainable High-Performance Hydraulic Concrete)

Abstract

:
Magnesium oxychloride cement (MOC) foam concrete (MOCFC) is an air-hardening cementing material formed by mixing magnesium chloride solution (MgCl2) and light-burned magnesia (i.e., active MgO). In application, adding caustic dolomite powder into light-burned magnesite powder can reduce the MOCFC production cost. The brine content of MOC changes with the incorporation of caustic dolomite powder. This study investigated the relationship between the mass percent concentration and the Baumé degree of a magnesium chloride solution after bischofite (MgCl2·6H2O) from a salt lake was dissolved in water. The proportional relationship between the amount of water in brine and bischofite, and the functional formula for the water-to-cement ratio (W/C) of MOC mixed with caustic dolomite powder were deduced. The functional relationship was verified as feasible for preparing MOC through the experiment.

1. Introduction

Magnesium oxychloride cement (MOC) is formed by mixing magnesium chloride solution (MgCl2–H2O) with magnesium oxide powder (MgO) [1,2]. As an air-dried gel material, MOC is widely used in several fields, including construction, transportation and technology [3,4,5,6]. At room temperature and pressure, the chemical reactions in the MgO-MgCl2-H2O system are the following:
5MgO + MgCl2 + 13H2O → 5Mg(OH)2·MgCl2·8H2O (5·1·8 phase)
3MgO + MgCl2 + 11H2O → 3Mg(OH)2·MgCl2·8H2O (3·1·8 phase)
MgO + H2O → Mg(OH)2
The above equations show that the hydration product of MOC depends on the ratio of the constituents, including the molar ratios of MgO/MgCl2 and H2O/MgCl2 [7]. At present, the MgO raw materials for MOC products are mostly light-burned magnesite (LMP), which can be made from magnesite calcined at 900 to 1050 °C [8,9]. The calcination of MgO allows the preparation of active magnesium oxide (MgOa), and the degree of crystallization of MgOa has a strong impact on the hydration reactions in MOC, determining the hydration products and its deformation and strength characteristics. With the continuous growth of the world’s requirements for magnesite and the environmental pressure, the price of LMP remains high. MgOa can be produced from the calcination of magnesite or dolomite [10,11]. Dolomite resources are widely distributed [12]. The economic cost of producing MOC can be effectively reduced by adding caustic dolomite powder (CDP) to the raw material of LMP. However, CDP cannot be directly applied to the production of MOC due to the MgO components. Dolomite calcinated at a lower temperature may generate calcination products of MgO with CaCO3 [13]. The MgO content in dolomite is one-third of that of magnesite; therefore, the mechanical performance of MOC prepared with dolomite raw material is poor [14], especially magnesium oxychloride cement foam concrete (MOCFC) made from porous material [15]. Dolomite has already been tested as a raw material for producing MgO-based cements such as magnesium oxychloride cement [16], magnesium oxysulfate cement [17] and magnesium phosphate cement [13]. However, few studies have been conducted using CDP and LMP as the raw materials to produce MOC material, and only a few scholars have probed the performance of MOC made from mixed materials [18]. The ratio between the mixed raw materials and the liquid phase still needs to be determined, as it is significant for the scale production of MOC.
The current raw bischofite (MgCl2·6H2O) for the MOC product is generally obtained from the byproduct of a potash fertilizer [19]. This is because the large amount of the byproduct bischofite in a salt lake area can substantially reduce the manufacturing cost of MOC. For example, in Qarhan Salt Lake, in Qinghai Province, potash production was about 3.7 million tons of K2O in 2011 and about 3.9 million tons of K2O in 2012, corresponding to an annual production of about 29 to 39 million tons of bischofite [20]. Salt Lake areas are enriched with a large quantity of bischofite resources that have not been exploited and utilized, which restricts the balance and sustainable development of local resources [21,22]. However, the impurity mass content of bischofite can be 2% or more; see Table 1. The strength of MOC can be reduced with the introduction of waste [14]. The MgCl2 used in the laboratory or small amounts of MgCl2 used to study MOC material are obtained as high-purity raw materials [23,24], and some errors may be involved in practical industrial applications when an impure raw material is used [25]. Due to the number of raw materials, their relationships with concrete performance have a great impact [26,27]. In order to use a large amount of bischofite for the scale production of MOC, it is necessary to find the relationship between the quantities of raw materials used for the scale production of MOC. This is of great significance for the popularization and application of economical MOC and its products in the salt lake regions.
Based on the above hypothesis, firstly, the relationship between the quantities of raw materials used in the preparation of MOC with single LMP and pure magnesium chloride were derived, and a derivation of formula (DF) was obtained. Secondly, the calculation method for the MOC raw material mix ratio was revised and simplified in accordance with the actual parameters of bischofite dissolved in water, and thereby, a modification of formula (MF) was obtained. Finally, according to the MF and the relationship between the amount of water in brine and bischofite, a water-to-cement ratio (W/C) function model when using CDP and LMP as the raw material for MOC simultaneously was derived, and the model was verified for MOCFC.

2. Materials and Methods

2.1. Raw and Processed Materials

The MOC raw materials were mixed with caustic dolomite fines, including the potassium byproduct of bischofite, LMP and CDP. The bischofite was produced in Qarhan Salt Lake of Qinghai province. The chemical composition of the bischofite is presented in Table 1. The LMP was produced in Haicheng of Liaoning province. The CDP was prepared in the laboratory. The dolomite ore was mined from Huzhu County, Qinghai Province, China, and its main components are CaMg(CO3)2, CaCO3 and SiO2. The CDP was obtained by calcining the dolomite ore in a Tunnel kiln at a temperature of 750 °C, grinding it and then screening it through a 120-mesh sieve. The main chemical constituents of the LMP and CDP were analyzed via X-ray fluorescence (XRF), and the results are presented in Table 2. According to the hydration method and citric acid method [7], the contents of MgOa of the LMP and CDP were 63.73% and 18.70%, respectively.

2.2. Brine Test

The mass percentage concentration (P), density (ρ) and Baumé degree (Ba) of MgCl2–H2O were tested by dissolving bischofite in tap water. The ρ and Ba were measured with an electronic densitometer and a Baumé meter, respectively. The test was performed three times at the same ambient temperature (20 °C), and the average value was obtained. The weighed bischofite was first placed in a measuring cylinder (1000 mL) and then slowly added to tap water until the bischofite was completely dissolved, at which point the solution was saturated in each test. Afterward, water was added to the saturated solution at 10 different times, so that the total amount of water added was 100 g. After each addition of water, the solution was stirred with a glass rod for 1 min. After the solution was evenly mixed, the Ba and ρ were measured. The amount of water (free water, mf) and chlorobalite (mBi) added to the solution at different stages affected the mf/mBi ratio, which in turn influenced Ba and ρ. For example, when mf/mBi = 0.55, the corresponding Ba and ρ were 31.0 and 1276, respectively. The results are presented in Table 3.

2.3. MOCFC Test

In the preparation of the MOCFC samples, first, bischofite was dissolved in water, and MgCl2–H2O of 25 °Be’ was prepared and was then mixed and stirred evenly with LMP. The foam (made from a commercially available animal protein foaming agent) was added to the MOC slurry, and the mixture was evenly mixed (the ratio of the volume of foam added to the mass of the slurry was 400). The mixture was cast in a 100 × 100 × 100 mm test mold. The specimens were covered with plastic film and cured at room temperature for 24 h. The specimens were then removed from the mold and cured in an environment of 20 ± 3 °C and relative humidity of 50% (air humidity). For the 28-day matured composites, the micromorphology and mechanical performance were determined. The micromorphology was characterized by scanning electron microscopy (SEM, JSM-5610LV) with gold coating. The mechanical performance was investigated with a universal testing machine (WDW-200Y, loading speed of 0.5 ± 0.05 MPa/s).

3. Results and Discussion

3.1. Derivation of Formula (DF)

The results show that a 5·1·8 phase was present in crosslinked needle- and rod-shaped crystals in the MOC, which endowed it with good mechanical properties [23,24]. When the molar ratio of MgO/MgCl2 was less than 6, the MgO content in the hydration products increased with an increase in the MgO/MgCl2 molar ratio, which made the original solution more alkaline and ensured the stability of the MOC phase [7]. It is generally believed that MOC products have excellent properties when the MgO/MgCl2 molar ratio is 5–10 [28,29,30]; nonetheless, in one study, the mechanical properties of MOC products were best when the molar ratio was approximately 7 [28,29]. Therefore, most researchers and manufacturers usually take the MgO/MgCl2 molar ratio as the benchmark parameter of the MOC system ratio in current MOC applications.
Let the MgO/MgCl2 molar ratio be n; then
n MO n MC = n
where nMO and nMC represent the molar masses of MgO and MgCl2, respectively.
The relationship between the MgO mass (mMO) and nMO and the relationship between the brine mass (mBr) and nMC can be deduced using Equations (5) and (6), respectively; in the equations, a is the amount of MgOa in the MgO powder:
n MO = a   m MO 40
n MC = P   m Br 95
where the molar mass of MgO is 40 g/mol and that of MgCl2 is 95 g/mol. By substituting Equations (5) and (6) into Equation (4), the relationship between the mBr and mMO can be obtained:
m Br m MO = 95   a 40   n P = 2.375   a n   P
Equations (5)–(7) represent the basic relationships of the MOC raw materials. n is defined by the material designer and is often fixed. Therefore, the performance of MOC is usually determined by a and P, with P obtained through Ba. The relationship between the Ba value of MgCl2–H2O and the ρ can be obtained by formula (8) [30]:
B a = [ 144.3 ( 144.3 γ ) ] = [ 144.3 ( 144.3 ρ / 1000 ) ]
where γ is the specific gravity.
When the Ba was measured, the ρ was calculated by Equation (5), and the P of the solution was obtained by comparing the solution density with the data in Table 4, obtained from a chemistry manual [31]. Equations (7) and (8) are also often used to calculate the ratio of MOC raw materials and the quantities of MOC materials. In the traditional preparation process for MOC, the relationship between brine and MgO can be calculated by Formulas (4)–(8) on the basis of obtaining the activity value of magnesium oxide and the molar ratio of MgO/MgCl2, and Formulas (4)–(8) can be regarded as the traditional derivation of the mixture ratio of MOC, namely, the derivation of formula (DF).
The above DF may be complicated because the ρ needs to be calculated, and the P needs to be determined. Technicians hope to obtain the brine dosage directly and simply in practical engineering applications. In addition, the raw material bischofite used in MOC products is usually a byproduct of potassium extraction from salt lakes and contains certain impurities and other components (Table 1). As the standard mass concentration for MgCl2 is defined using high-purity raw materials, in practical industrial applications, errors may occur when impure raw materials are used to define the standard. The error caused by this impurity leads to the deviation of the final dosage of bischofite or brine in practical applications.

3.2. Modification of Formula (MF)

Due to the large unit scale value of Ba and its easily accessible data, to accurately control the brine concentration and the dosage in MOC raw materials, the Ba is usually used to calculate the mass percentage concentration of the solution in industrial production. Therefore, to avoid the lengthy process and errors caused by the application of P, it is necessary to establish a connection between Ba and a in the scale production of MOC.
In Table 3, the P and Ba of the MgCl2–H2O formed by the dissolution of bischofite from water at ambient temperature (20 °C) exhibited a linear growth trend, and the average difference between them was 0.9. The relationship between the Ba of bischofite in tap water and its P can be defined as
Avg .   ( B a i P i ) = 0.9 ,   ( i = 1 , 2 , 3 )
The data in Table 4 were from the standard manual [31]. In the standard data, the average [Bai* − Pi*] = 0.7, which deviates from the test data (Equation (9)) by 0.2. This deviation occurs because the bischofite in salt lake water contains some impurities, which affect the P of MgCl2–H2O. Based on the above tests, when bischofite is used as the liquid phase material of MOC, (Ba − 0.9) can be directly used to replace P. Equation (9) was substituted into Equation (7) to obtain the MF applicable to the ratio of bischofite to the MOC material:
m Br m MO = 2.375   a n   ( B a 0.9 )
After the simplification of the DF, the relationship between brine and MgO can be calculated by formula (10) on the premise of obtaining the magnesium oxide activity value and the molar ratio of MgO/MgCl2; therefore, the Formula (10) is the modification of formula (MF).

3.3. Relationship between the Amount of Water in Brine and Bischofite

MgCl2–H2O of a certain concentration was formed after the bischofite solution was dissolved in water. The water in the solution comes from the crystal water in bischofite and the free water in dissolved bischofite; that is, the total amount of water (mHO) was the sum of the crystal water (mj) and free water (mf), as shown in Equation (11).
mj + mf = mHO
It can be seen from Equation (11) that MgCl2–H2O of different concentrations was formed after bischofite was dissolved in water, and the proportional relationship between the added mf and the bischofite mass (mBi) can be expressed as follows:
m f m Bi = m HO m j m Bi
From the mass percentage concentration expression, the mass ratios of H2O and MgCl2 in MgCl2–H2O can be deduced:
P = m MC m MC + m HO = > m HO m MC = 1 P 1
The relationship between the mass of water and MgCl2 in solution and the Ba was obtained by substituting (9) into (13).
m HO m MC = 1 ( B a 0.9 ) / 100 1
The molecular weights of bischofite, MgCl2, and 6H2O are 203, 95 and 108, respectively; therefore, the masses of MgCl2 and its mj were, respectively,
m Bi = m MC ÷ 95 203 = 2.1368   m MC
m j = m MC ÷ 95 203 × 108 203 = 1.1368   m MC
By substituting Equations (14)–(16) into Equation (12), the proportional relationship between mf and the bischofite in the solution was obtained:
m f m Bi = 1 0.021368   ( B a 0.9 ) 1
When bischofite was dissolved in water, MgCl2–H2O of a certain concentration was formed. The ratio of mf added to the bischofite was a function of the Ba: f(mf/mBi) = f(Ba), which can be calculated according to Equation (17). As shown in Table 3, the actual measured function is expressed as f(mf/mBi) = f(Ba). As shown in Table 4, the Standard data is expressed as f(mf/mBi)*. The calculated proportion and the actual proportion fitting curves are displayed in Figure 1. The fitting curves obtained by the two methods were approximate, and the calculated proportion fitting curve was slightly higher than the actual proportion fitting curve. This was mainly because in the actual measurement process, there may be some deviation in the fractional part of the Ba reading. For example, when f(mf/mBi) = 1.02, the test Ba was 24.2 °Be’, while the accuracy of 0.2 °Be’ showed some deviation in the reading, resulting in a slightly higher computational proportion simulation curve.

3.4. Water-to-Cement Ratio (W/C) with Caustic Dolomite MOC

Previous studies have proved that MOC products have the best performance when the optimal molar ratio of MgOa/MgCl2 approaches n = 7 [28,29]. At present, most manufacturers fix the raw material molar ratio at around 7. To maintain this constant, different concentrations of MgCl2–H2O and dosage should be determined in tests or production according to the activity of magnesia powder. However, the active content and composition of industrial LMP usually change, and when CDP is added to LMP, the concentration and dosage of MgCl2–H2O change again. Therefore, the best method was to analyze the brine consumption by CDP–MOC via quantitative analysis and variable analysis; that is, the total water consumption in MOC was divided into three parts: mj, mf and mt. Among them, the mt was the internal water of the bischofite. When bischofite was dissolved in water, the mt also turned into a solvent and was used for the quantitative analysis. The mf was the amount of water added to prepare bischofite at a certain concentration, and it changes with the brine concentration; thus, it was used for semiquantitative analysis. It reacts with mf in the MOC system with MgOa and MgCl2 to form the 5·1·8 phase. The mt plays a role in regulating the workability of MOC slurry, which is completely dependent on the composition of MgO; the water was used for the variable analysis. Since the external water of MOC comprised mf and mt, the W/C of MOCFC can be expressed as
f ( W C ) = m f + m t m MO = > f ( W C ) = m f m MO + m t m MO
Equation (17) was substituted into Equation (18) to obtain
f ( W C ) = ( 1 0.021368   ( B a 0.9 ) 1 )   m Bi m MO + m t m MO
Since the mass of MgO consisted of CDP and LMP in the MOCFC system, the MgOa was also divided into two parts: the MgOa of CDP and the MgOa of LMP. Let the MgOa of CDP and LMP be a1 and a2, respectively, and the mixing ratio of CDP and LMP be x:y; then, according to (10), the proportional relationship between the mBr and mMO in MOC with dolomite can be deduced as
m B r m M O = 2.375   x   a 1 + y   a 2 n   P   ( x + y )
Since the mMC in MgCl2–H2O was the product of the mBr and P, Equations (14) and (20) were substituted into Equation (19) to obtain
f ( W C ) = 5.0749   ( 1 0.021368   ( B a 0.9 ) 1 ) x   a 1 + y   a 2 n   ( x + y ) + m t m MO
It can be seen from Equation (21) that the W/C in the MOC was composed of two parts. The ratio of mf to MgO was a function of Ba and MgOa, and the ratio of mt to MgO was a function of the volume of the mt:
f ( W C ) = f ( B a ) + f ( m t )

3.5. Calculation Example

By means of the MF and brine relationship, the W/C relationship of LMP and CDP as MOC raw materials was obtained. Is this relationship feasible in the large-scale production of MOC? It also needs to be verified in actual production. As a result, ten groups of tests were used to verify the applicability of Equation (21), taking MOCFC as an example. The optimal molar ratio was set at 7 [7,24], the brine concentration was set at 25 °Be’, and the foam volume added was 400 times the mass of MgO raw material according to the above analysis. Since it is easy to obtain MOCFC with excellent mechanical performance when W/C = 0.5–0.6, samples with different x:y ratios at W/C = 0.45–0.63 were selected for intensity testing (as shown in Figure 2). The intensity of MOCFC with different x:y ratios increased with W/C at the beginning and then decreased after reaching the peak. Generally speaking, within a suitable W/C range, the higher the content of MgOa in the raw material is, the easier it is to obtain MOCFC with higher intensity. When the content of dolomite is relatively high, for example, x:y = 5:1, it is easier to obtain stable mechanical performance. When W/C < 0.51, given the high proportion of MgOa in the raw materials and the low water content, the MOC slurry has a large amount of heat of hydration and undermixed powder, which makes it difficult to add foam into the slurry and impossible to shape the MOCFC. From the W/C mechanical performance test (Figure 2), it can be concluded that for MOCFC with CDP and LMP being the raw materials, MOCFC with the best performance can be obtained when W/C = 0.45–0.63.
According to Equation (21), the f(Ba) at the mixing ratios of CDP and LMP of 2:1, 3:1, 4:1 and 5:1 can be calculated as 0.18, 0.16, 0.15 and 0.12, respectively. Since f(Ba) is a fixed value calculated according to the formula, according to Equation (22), the mechanical performance of MOCFC changes with f(mt). As shown in Figure 3, the strengths of four MOCFC specimens with different mix ratios changed with a change in f(mt), and the f(mt)s of the specimens that reached the optimal strength were 0.35, 0.37, 0.38 and 0.37. According to Equation (21), the optimal W/Cs for MOCFC were 0.53, 0.53, 0.52 and 0.49. The higher the MgOa in the raw material for the MOC system, the greater the water consumption. The MgOa among the four mixing ratios was of the following order: 2:1 > 3:1 > 4:1 > 5:1, which was consistent with the W/C trend obtained in the experiment.
The typical morphology of the x:y = 2:1 sample is shown in Figure 4. In the picture, the red arrows are pin-needle-like 5·1·8 phase crystals [7,30], the blue arrows are Mg(OH)2 [32], and the purple arrows are bubble holes. The varied morphology of six types of MOCFC can be seen in the images. It is apparent that those in Figure 4a–c were covered with a thicker and larger 5·1·8 phase in the bubble hole wall compared to those in Figure 4d–f. This contributed to the highest compressive strength of the controlled sample. When f(mt) = 0.35, the bubble hole wall seems to have consisted entirely of 5·1·8 phases. As f(mt) increased, the 5·1·8 phase in the bubble wall gradually decreased, while the Mg(OH)2 gradually increased. This happened because with excessive water, the MgOa generates more Mg(OH)2, which leads to a decrease in the intensity of the samples. We can see in Figure 4a that the walls of the bubble holes were covered by 5·1·8 phase crystals, while in Figure 4b,c, it can be seen that small amounts of flake-like Mg(OH)2 began to occur, and in Figure 4e,f, it can be observed that Mg(OH)2 was so abundant that it also covered the bubble holes. The size of the 5·1·8 phase showed the trend of 0.35 > 0.37 > 0.39 > 0.41 > 0.43 > 0.45 in the bubble wall and the opposite trend in Mg(OH)2. A linear increasing relationship between the number of 5·1·8 phase crystals and the proportion of W/C was shown, while Mg(OH)2 showed the opposite trend. Combining the results in Figure 2, when the W/C was increased from 0.51 to 0.63, the strength of the sample (x:y = 2:1) gradually decreased. W/C = 0.54 had the highest compressive strength (Figure 2); the corresponding 5·1·8 phase crystals were the highest (Figure 4a), while when W/C = 0.63, the compressive strength was the lowest (Figure 2), and the corresponding Mg(OH)2 reached the highest (Figure 4e). The results observed from the SEM photo are consistent with those of the compressive strength test.
In previous work, it was suggested that the W/C of MOCFC with LMP ranged from 0.5 to 0.6, and the optimal test W/C was 0.55 [33,34]. These data are approximately equivalent to the findings in the current study, though the difference is that the activity of the doped CDP was less than that of the raw material; therefore, the W/C was less than 0.55, which also reflects the amount of brine and powder in the MOCFC of the real raw material. Combined with the actual preparation process for MOCFC, the “modification of formula” and the W/C relationship deduced above were feasible for the large-scale preparation of MOC using CDP and Salt Lake bischofite. The reason was that this model relationship shows the mechanical properties and corresponding microstructure initially involved in the above examples. The model relationship has the ability to truly reflect the material dosage relationship on the premise of ensuring the performance of MOC materials.

4. Conclusions

  • The physical properties of salt lake bischofite dissolved in water were first studied in this research. The P and Ba of MgCl2–H2O formed by bischofite dissolved in water showed a linear growth trend at ambient temperature (20 °C), and the average difference between the two was 0.9.
  • The ratio relationship between the mBr and mMO in MOC with dolomite was obtained using the mean difference (Avg.(BaiPi = 0.9)) and the MF: mBr/mMO = 2.375 [(x a1 + y a2)/n P (x + y)]. Then, the proportional relationship between the mf added to bischofite was deduced, and the proportional relationship function was obtained: f(mf/mBi) = 1/0.021368 (Ba − 0.9) − 1.
  • According to the MF, f(mBr/mMO) and the proportional relation function (f(mf/mBi)), the W/C relation formula for MOC with CDP was summarized: f(W/C) = f(Ba) + f(mt). It was verified through experiments that the W/C relationship of CDP–MOC can reflect the dosage relationship between the brine and powder in MOCFC under the conditions of real raw material ratios.
  • The derived MF formula and W/C relationship were verified in the practical production of MOCFC, and the optimum W/C range for MOCFC was obtained by using the W/C formula. It can be concluded that, for MOCFC with CDP and LMP being the raw materials, MOCFC with the best performance can be obtained when W/C = 0.45–0.63. The MgOa among the four mixing ratios was of the following order: 2:1 > 3:1 > 4:1 > 5:1, which was consistent with the W/C trend obtained in the experiment. As f(mt) increased, the 5·1·8 phase in the bubble wall gradually decreased, while the Mg(OH)2 gradually increased. This happened because with excessive water, the MgOa generates more Mg(OH)2, which leads to a decrease in the intensity of the samples.

Author Contributions

All authors discussed and agreed upon the idea, and made scientific contributions: writing—original draft preparation, W.Z. and X.X.; experiment designing, J.W.; experiment performing, C.C. and S.A.; data analysis, W.Z.; writing—review and editing, W.Z. and J.D. All authors have read and agreed to the published version of the manuscript.

Funding

This research was funded by the Fund of Key Lab of Plateau Building and Eco-Community in Qinghai, China (2019-SL-001), and supported by the fund of Applied Basic Research Project of Qinghai Province, China (2021-ZJ-750, 2020-ZJ-746), and the High-End Innovative Talents Thousand Talents Plan of Qinghai Province, China.

Institutional Review Board Statement

Not applicable.

Informed Consent Statement

Not applicable.

Data Availability Statement

No new data were created or analyzed in this study. Data sharing is not applicable to this article.

Conflicts of Interest

The authors declare no conflict of interest.

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Figure 1. The ratio of free water to bischofite.
Figure 1. The ratio of free water to bischofite.
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Figure 2. Compressive strength of magnesium oxychloride cement foam concrete (MOCFC) specimens cured in air.
Figure 2. Compressive strength of magnesium oxychloride cement foam concrete (MOCFC) specimens cured in air.
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Figure 3. Compressive strength of MOCFC with different mix proportions on day 7.
Figure 3. Compressive strength of MOCFC with different mix proportions on day 7.
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Figure 4. SEM images of MOCFC. (af) are samples of f(mt) equal to 0.35, 0.37, 0.39, 0.41, 0.43 and 0.45, respectively.
Figure 4. SEM images of MOCFC. (af) are samples of f(mt) equal to 0.35, 0.37, 0.39, 0.41, 0.43 and 0.45, respectively.
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Table 1. Chemical composition of bischofite (wt.%).
Table 1. Chemical composition of bischofite (wt.%).
ComponentMgCl2KClNaClCaCl2MgSO4Water InsolublesCrystal Water
Bischofite46.100.380.460.110.090.4552.41
Table 2. Chemical composition of light-burned magnesite (LMP) and caustic dolomite powder (CDP) (wt.%).
Table 2. Chemical composition of light-burned magnesite (LMP) and caustic dolomite powder (CDP) (wt.%).
ComponentMgOSiO2CaOAl2O3Fe2O3Loss on Ignition
LMP *85.966.031.291.280.574.87
CDP *20.151.4633.200.850.4743.87
* The contents of MgOa in LMP and CDP were 63.73 and 18.70, respectively.
Table 3. Test data of the brine.
Table 3. Test data of the brine.
mf/mBiBa (°Be’)Ρ (kg/m3)P (%)
0.5531.0127629.7
0.6928.0125627.9
0.8026.5123926.3
0.8425.5122424.9
1.0024.2121223.6
0.9923.0120122.4
1.1122.0119121.4
1.3021.0118220.5
1.3320.0116719.6
1.4519.5116518.8
1.5019.0115818.0
mf/mBi represents the mass ratio between the tap water and bischofite; P was calculated according to Table 1; P = (mMC × 46.10%)/[mHO + mMC × (100 − 46.10)%] × 100%; mMC and mHO are the masses of MgCl2 and H2O in the solution.
Table 4. Standard data of the brine.
Table 4. Standard data of the brine.
P * (%)ρ * (kg/m3)Ba * (°Be’)Bai * − Ci *
21014.62.10.1
41031.13.3−0.7
61047.86.60.6
81064.68.80.8
101081.610.90.9
121098.913.01.0
141116.415.01.0
161132.416.80.8
181152.319.01.0
201170.621.11.1
251218.425.80.8
301268.830.60.6
* Standard data from manual.
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Zheng, W.; Xiao, X.; Wen, J.; Chang, C.; An, S.; Dong, J. Water-to-Cement Ratio of Magnesium Oxychloride Cement Foam Concrete with Caustic Dolomite Powder. Sustainability 2021, 13, 2429. https://doi.org/10.3390/su13052429

AMA Style

Zheng W, Xiao X, Wen J, Chang C, An S, Dong J. Water-to-Cement Ratio of Magnesium Oxychloride Cement Foam Concrete with Caustic Dolomite Powder. Sustainability. 2021; 13(5):2429. https://doi.org/10.3390/su13052429

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Zheng, Weixin, Xueying Xiao, Jing Wen, Chenggong Chang, Shengxia An, and Jingmei Dong. 2021. "Water-to-Cement Ratio of Magnesium Oxychloride Cement Foam Concrete with Caustic Dolomite Powder" Sustainability 13, no. 5: 2429. https://doi.org/10.3390/su13052429

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