Issue
Natl Sci Open
Volume 3, Number 3, 2024
Special Topic: Energy Systems of Low Carbon Buildings
Article Number 20230056
Number of page(s) 48
Section Engineering
DOI https://doi.org/10.1360/nso/20230056
Published online 09 January 2024

© The Author(s) 2024. Published by Science Press and EDP Sciences.

Licence Creative CommonsThis is an Open Access article distributed under the terms of the Creative Commons Attribution License (https://creativecommons.org/licenses/by/4.0), which permits unrestricted use, distribution, and reproduction in any medium, provided the original work is properly cited.

INTRODUCTION

Addressing climate change is a major challenge worldwide. Building energy consumption is a significant contributor to global energy consumption and CO2 emissions, with approximately 50% of this demand attributed to thermal energy requirements, notably space heating and domestic water supply. As demonstrated in Figure 1A, cities in Northern China exhibit exceptionally high annual heating demands, with over 54.9% of them having annual heating intensities exceeding 100 kWh/(m2 a) [1]. Moreover, at the national level, the total CO2 emissions from centralized building heating maintained an increasing trend [2], with per capita CO2 emissions from space heating and domestic water heating accounting for a substantial 78% of the total emissions [3], as shown in Figure 1B and C.

thumbnail Figure 1

Thermal energy demand in China. (A) Annual heating intensity in north urban China in 2020 [1]. Copyright © 2023, Springer Nature Limited. (B) Historical CO2 emissions from centralized heating at the national level [2]. Copyright © 2023, Elsevier. (C) Residential end-use CO2 emissions in urban areas [3]. Copyright © 2023, Elsevier.

The pursuit of reduced building energy consumption has spurred extensive research into phase change materials (PCMs), as visually depicted in Figure 2. PCMs serve as thermal energy storage (TES) mediums, capable of absorbing and releasing thermal/cold energy through alterations in their physical states. This property enables PCMs to effectively store solar energy during periods of abundant solar radiation and subsequently release heat as needed, thereby significantly mitigating building heating demands [4,5]. Furthermore, as elucidated in Figure 3, PCMs can be broadly categorized into three types based on their state transitions during the phase change process: liquid-gas PCMs, liquid-solid PCMs, and solid-solid PCMs. It is noteworthy that salt hydrate PCMs offer several advantages [6], including high thermal conductivity, versatile operating temperature ranges, cost-effectiveness, non-toxicity, and non-flammability, summarized in Table 1. Consequently, salt hydrate PCMs hold substantial promise for large-scale engineering applications.

thumbnail Figure 2

Investigation of PCM applications in buildings. (A) Cluster analysis graph depicting the keywords “reduce building energy consumption” and “material” using VOS viewer. (B) Number of publications on the keyword “phase change material” from 2000 to 2023 (data as of September 2023 from Web of Science). (C) Schematic diagram illustrating the relationship between heat gain and building heat demand.

thumbnail Figure 3

Classifications of PCMs.

Table 1

Comparison between organic PCMs and salt hydrate PCMs

PCMS-ENHANCED BUILDING ENERGY STORAGE SYSTEMS

Currently, substantial research has focused on three categories of energy storage systems leveraging PCMs in buildings, as depicted in Figure 4. These categories include PCMs-enhanced building facilities, PCMs-enhanced building envelopes, and PCMs-enhanced geostructures [4,5,711]. PCMs-enhanced building energy storage systems enable the storage of thermal or cold energy during off-peak periods, releasing it during peak demand times, effectively reducing overall energy demand within buildings [5,10]. However, it is crucial to note that PCMs must be tailored to meet precise temperature requirements during their applications. For facility systems, PCMs must exhibit a suitable phase change temperature. In thermal storage applications like domestic hot water, PCMs with a melting temperature (T m) typically within 45–50°C enhance the coefficient of performance (COP) of heat pump systems [5,12]. This aligns with the maximum temperature achievable by conventional air-source heat pumps, approximately 55°C [13]. For cold storage, PCMs should have a proper crystallization temperature, typically within 7–10°C, aligning with the lowest temperature achievable by conventional chiller cooling water, approximately 5°C [14].

thumbnail Figure 4

Schematic of various PCMs-enhanced energy storage systems in buildings. (A) PCMs-enhanced centralized thermal/cold storage systems. (B) PCMs-enhanced solar harvesting/heat pump energy storage systems. (C) PCMs-enhanced photothermal energy storage wall/roof structures. (D) PCMs-enhanced thermoregulated wall/floor components. (E) PCMs-enhanced energy piles and (F) PCMs-enhanced energy tunnels. Adapted with permission from refs. [4,5,711], Copyright © 2023, Elsevier, Copyright © 2022, Elsevier, Copyright © 2022, Elsevier, Copyright © 2022, Elsevier, Copyright © 2022, Elsevier, Copyright © 2018, Elsevier, Copyright © 2019, Elsevier.

For applications like heat storage in drying agricultural or food products, PCMs with phase change temperatures within 50–60°C are suitable. Conversely, for indoor temperature regulation, their phase change temperatures should align with thermal comfort, typically within 20–28°C [4,7,15,16]. When PCMs enhance the energy density of geostructures, their temperature characteristics become pivotal. Specifically, for shallow geothermal energy, PCMs should operate within the temperature range of 8–28°C, while for low ground temperature geothermal energy, the range should be within 0–20°C. This aligns with the operational requirements of cold/heat energy demand for the above-ground construction [9,17]. Therefore, it is evident that low-temperature salt hydrate PCMs play a vital role as latent heat storage materials in contemporary research. Table 2 presents a compilation of various types of salt hydrate PCMs that meet the temperature requirements of the building energy storage systems mentioned above.

Table 2

Types of low-temperature salt hydrate PCMs (below 120°C) a [1820]

CHALLENGES ASSOCIATED WITH THE APPLICATIONS OF SALT HYDRATE PCMS

While the utilization of salt hydrate PCMs in various building energy storage systems holds promise for reducing overall energy consumption, several challenges must be addressed before their practical engineering applications, as shown in Figure 5. The first significant challenge pertains to their poor nucleation characteristics, leading to substantial supercooling degree and impeding efficient energy storage charging. The second challenge revolves around phase separation, a consequence of the incongruent melting behavior of salt hydrates during the phase change process. As the number of energy storage cycles increases, solid salt gradually accumulates at the container’s bottom and, due to gravitational forces, does not redissolve into water during the melting process. The third challenge lies in the inadequate thermal conductivity of PCMs (below 0.7 W/(m K)). While their thermal conductivity surpasses that of organic PCMs, achieving higher thermal conductivity remains desirable to enhance heat exchange efficiency further. The fourth challenge concerns the ability to control the phase change temperatures of salt hydrates, making them suitable for diverse energy storage systems. Lastly, salt hydrates are corrosive to metals, potentially leading to leakage in metal containers used for heat exchange enhancement and corrosion of metal fins employed for thermal conductivity enhancement.

thumbnail Figure 5

Challenges of utilizing salt hydrate PCMs in buildings.

REVIEW FRAMEWORK

Over the last few years, several review papers have been published to consolidate the periodic accomplishments in salt hydrate research. Wong-Pinto et al. [19] and Zahir et al. [21] delved into the supercooling of salt hydrates, particularly in the context of optimization with nanomaterials and triggering techniques. Kumar et al. [22], Schmit et al. [23], Yu et al. [24], and Liu et al. [25] focused on topics such as thermal conductivity enhancements, phase transition enthalpies, and shape stabilization of salt hydrates. However, these existing reviews have omitted a critical analysis of salt hydrate modification methods and their underlying mechanisms. Consequently, this paper seeks to comprehensively review these mechanisms before and after the optimization of salt hydrates, drawing insights from existing literature across five key areas: supercooling, phase separation, thermal conductivity, phase change temperature, and metal corrosion, as illustrated in Figure 5.

SUPERCOOLING

Supercooling represents a metastable state of PCMs, wherein they remain in a liquid phase below the melting temperature without an instantaneous release of latent heat of fusion. The stability of supercooled solutions is often assessed using the hydrochemical potential as an indicator, with Eq. (1) illustrating this relationship:

μ H 2 O = μ c μ m = μ s μ m = R T ln a s a m , (1)

where am , as , and T denote the supercooled water activity, water activity of saturated solution, and storage temperature, respectively; μ H 2 O denotes the difference in water chemical potential (the supercooled solution is stable when μ H 2 O > 0 ); μc, μm, and μs denote the chemical potential of hydrated salt crystals, the chemical potential of the supercooled solution, and the chemical potential of saturated hydrated salt solution, respectively.

Upon demand, the supercooled solution can be triggered to coagulate and crystallize, releasing the latent heat of melting and enabling long-term stable TES [26]. Take sodium acetate trihydrate (SAT) as an example, Dannemand et al. [27] and Johansen et al. [28] utilized stable supercooled solution to achieve trans-seasonal heat migration with low heat loss over a period of about two and five months, respectively. However, the metastable nature of supercooled solutions makes them susceptible to impurities and external disturbances, including the supercooling stabilizer [29], container design [30], and external environment [31]. Premature crystallization leads to ineffective energy consumption in the overall system [32], particularly in large-volume thermal storage systems [33]. In contrast, short-term flexible TES is more desirable for a broader range of applications.

The metastable state of PCMs is generally unsuitable for short-term flexible TES, impeding their rapid thermal storage/release in high-efficiency applications [21,34]. Researchers have quantified this phenomenon by characterizing the supercooling degree, which denotes the disparity between the T m and the solidification temperature (T s), as illustrated in Figure 6A. Over the past few decades, numerous strategies have been developed to minimize this undesirable supercooling effect. These strategies include the use of additives, external field control, and various other methods [35], with additives emerging as the prevailing and cost-effective approach in current research [36]. Effectively mitigating the supercooling tendencies of salt hydrates requires a comprehensive understanding of their nucleation mechanisms, as depicted in Figure 6B, showcasing various methods and summarizing current research progress in this area.

thumbnail Figure 6

Schematic illustration of nucleation mechanisms of salt hydrate PCMs. (A) Schematic of temperature vs. time curve measured by T-history method and (B) nucleation methods to promote the crystallization of salt hydrate PCMs.

Anti-supercooling mechanism based on the classical nucleation theory

The classical nucleation theory (CNT) stands as the most widely accepted theoretical model for the investigation of crystal nucleation. It encompasses two primary nucleation processes: homogeneous and heterogeneous nucleation [37]. Therefore, this section primarily delves into homogeneous and heterogeneous nucleation through the lens of Gibbs free energy to elucidate the mechanism behind countering supercooling in salt hydrate PCMs. The Gibbs free energy is a pivotal factor in determining the direction of thermodynamic processes. If the Gibbs free energy is negative under constant temperature and pressure, an isothermal or isostatic reaction is considered spontaneous; otherwise, it is non-spontaneous. When the Gibbs free energy is zero, the reaction is in equilibrium. Hence, the reduction of Gibbs free energy is typically regarded as the driving force behind the transition from liquid to solid phases.

Homogeneous nucleation

Homogeneous nucleation is a spontaneous and random process where the probability of a crystal nucleus forming from a uniform single-phase solute is uniformly distributed. According to the Gibbs free energy theory, the formation of crystals hinges on the difference between the volume free energy (ΔG V) and surface energy (ΔG S) of the emerging nucleus, as illustrated in Figure 7A. Equation (2) delineates the change in free energy during the transition from a liquid to a solid state. In this process, ΔG V serves as the driving force, while ΔG S represents the barrier force. Figure 7B illustrates how Δg can be calculated as outlined in Eqs. (3)–(5), and Figure 7C presents the schematic diagram of the crystal growth process.

thumbnail Figure 7

Variation of Gibbs free energy for a transition from the liquid state to solid state. (A) Relationship between the nucleation radius and Gibbs free energy. (B) Relationship between the temperature and Gibbs free energy. (C) Labile-cluster model of hydrate nucleation [37]. Copyright © 2020, Royal Society of Chemistry. Note: ΔG denotes the Gibbs free energy; ΔG(r c) denotes the Gibbs free energy corresponding to the critical radius; Δg and ΔT denotes the difference in free energy per unit volume and supercooling degree of PCMs, respectively.

The variation mentioned is written as [38]

G = G V + G S = V g + A σ = 4 π r 3 g / 3 + 4 π r 2 σ , (2)

where Δg denotes the difference in free energy per unit volume between the liquid and solid states when thermodynamic phase nucleation occurs, and σ indicates the surface tension of the interface between the nucleus and its surroundings. The components of the above equations are as follows:

g = G ss G ls = H ss + T S ss H ls + T S ls = H T S , (3)

S = H / T m , (4)

g = H T / T m , (5)

where ΔG ss and ΔG ls denote the Gibbs free energies of the solid and liquid states of the PCM, respectively; ΔH ss and ΔH ls denote the enthalpies of the solid and liquid states of the PCM, respectively; ΔS ss and ΔS ls denote the entropies of the solid and liquid states of the PCM, respectively.

When ΔG S reaches its maximum value, the critical radius (r C) can be determined by taking its derivative, such that ΔG = 0, expressed as

r C = 2 σ / g = 2 T m σ / H T . (6)

This implies that only nuclei larger than a critical nucleus size are thermodynamically stable and capable of growing to a detectable size, while smaller nuclei dissolve. In the initial stages of crystal nucleation, PCM molecules diffuse to the forming nucleus and adhere to its surface. Consequently, these minute crystals continue to expand through this mechanism, gradually reaching a size where they can sustain rapid crystal growth [37,39,40].

From Eq. (6), it is evident that, under constant pressure, crystals can only form after the salt hydrate PCMs have undergone the supercooling stage. Considering Eqs. (2)–(6), it can be deduced that the minimum Gibbs free energy for the formation of crystals must satisfy the following Eq. (7) [41]:

G ( r C ) = 16 π T m σ 3 / 3 H 2 T 2 . (7)

Heterogeneous nucleation

Unlike homogeneous nucleation, which occurs spontaneously and randomly within a uniform solution, heterogeneous nucleation takes place on foreign particles or sites. These sites could include the container wall, impure particles, or unmelted crystal grains present in the liquid salt hydrates [34]. Besides, the crystal particles of nucleating agents or nuclei are formed by the liquid salt hydrates. From Figure 8A, it can be deduced that the Gibbs free energy of heterogeneous nucleation process can be expressed as the following equations [817]:

thumbnail Figure 8

Schematic of the contact angle between the crystal nucleus, liquid medium, and substrate surfaces for different structures. (A) The nucleus growing on the surface of a flat substrate [42]. Copyright © 2022, Elsevier. (B) The nucleus growing on the substrate surface under different structures for identical nucleation radii and contact angles.

The process mentioned is written as [4,42]

G S = A nl σ nl + A ns σ ns A sl σ sl , (8)

σ sl = σ nl cos θ + σ ns , (9)

A ns = A sl = π r 2 sin 2 θ , (10)

A nl = 2 π r 2 ( 1 cos θ ) , (11)

G S = 2 π r 2 ( 1 cos θ ) σ nl π r 2 sin 2 θ cos θ σ nl , (12)

V = π r 3 ( 2 3 cos θ + cos 3 θ / 4 ) , (13)

G = G V + G S = V g + A σ = ( 4 π r 3 g / 3 + 4 π r 2 σ nl ) f ( θ ) , (14)

f ( θ ) = 2 3 cos θ + cos 3 θ / 4 , (15)

r C = 2 σ / g = 2 T m σ / H T , (16)

G heterogeneous = G homogeneous f ( θ ) = 16 π T m σ 3 3 H 2 T 2 f ( θ ) ,    0 < f ( θ ) < 1 , (17)

where θ denotes the contact angle between the crystal nucleus and substrate surface; A nl, A ns, and A sl denote the surface areas between the crystal-nucleation and liquid phases, crystal-nucleation and substrate surfaces, and substrate surface and liquid phase, respectively; σ nl, σ ns, and σ sl denote the surface energy between the crystal-nucleation and liquid phases, crystal-nucleation and substrate surfaces, and substrate surface and liquid phase, respectively.

The critical radius of heterogeneous nucleation matches that of homogeneous nucleation, as determined from Eqs. (16) and (17). However, the key distinction lies in the Gibbs free energy, which is lower for heterogeneous nucleation compared with homogeneous nucleation, and this difference depends on the contact angle. Consequently, it can be inferred that the nucleation barrier for heterogeneous nucleation is significantly lower than that for homogeneous nucleation.

In addition to the supercooling degree and contact angle, the substrate surface morphology has also been identified as a factor influencing crystal crystallization, as illustrated in Figure 8B. When the critical radius and contact angle are the same, the volume of the nucleus, which must reach the critical radius, varies based on different interface morphologies. The concave surface exhibits the highest nucleation efficiency as it can most readily reach the critical radius of the crystal nucleus and requires a smaller embryo volume. Following this, the plane curvature efficiency is moderate, while the efficiency of the convex surface is the lowest. Consequently, the degree of supercooling varies depending on the surface morphology of the same type of nucleating agent.

Other influences on supercooling

In the CNT theory, the degree of supercooling in salt hydrates is primarily influenced by the contact angle and the morphology of the substrate. However, there are additional factors that can impact supercooling. Both Kubota et al. [43] and Lopez et al. [44] observed a size effect on the degree of supercooling during phase transitions in a KNO3 aqueous solution and VO2 nanoparticles, respectively. They found that smaller samples exhibited a higher degree of supercooling compared with larger ones. This phenomenon is attributed to the reduction in the total number of nucleation sites as the sample size decreases, leading to a lower likelihood of nucleation. According to the CNT theory, Reference [45] presented that the probability of successful nucleation at a specific temperature P(T) can be described by Eq. (18).

P ( T ) d T = 1 exp [ C | T H / T m | y V ] , (18)

where P(T) denotes the likelihood of successful nucleation at specific temperatures; C, y and V denote a proportionality constant, an exponent, and the test sample volume, respectively.

A higher cooling rate has been found to increase the degree of supercooling [46]. In the experiment conducted by Taylor et al. [47] using commercial hydrated calcium chloride salts, it was observed that the degree of supercooling rises with an increase in the cooling rate, as illustrated in Figure 9A. A similar phenomenon was reported by Solomon et al. [48], who attributed the change in PCM solidification temperature to the cooling rate (Figure 9B). Mollova et al. [45], in experiments with PCMs under varying cooling rates (ranging from 0.01 to 500 K), noted that higher cooling rates led to increased supercooling. This can be explained by either the growth of crystals, which depends on the crystal growth rate and takes time, or a significant reduction in the nucleation rate at lower temperatures. Oike et al. [49] further expanded on this by proposing that both the cooling rate and the volume of specimens significantly impact the degree of supercooling. They speculated that the sample volume to cooling rate ratio is closely related to the likelihood of nucleation at a specific temperature and developed a prediction model described in Eq. (19).

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Effect of cooling rate. (A) Supercooling degree as a function of cooling rate (the dashed lines give the linear trends of the data) [47]. Copyright © 2016, Elsevier. (B) DSC analysis of commercial PCM for different cooling rates [48]. Copyright © 2013, Elsevier.

P ( T ) d T = i v hetero ( T ) ( V / r ) d T exp [ ( V / r ) T T m i v hetero ( T ) d T ] , (19)

where i v hetero(T) and r represent the heterogeneous nucleation rate density and cooling rate, respectively.

Anti-supercooling optimization methods

Various methods have been explored to mitigate supercooling in salt hydrate PCMs, with a focus on promoting heterogeneous nucleation. Both internal and external factors impact crystallization, including the supercooling degree, contact angle, nucleation rate, and crystal growth rate. External factors like the sample volume and cooling rate also play a role in influencing supercooling. These factors contribute to different supercooling degrees for the same types of salt hydrates, even when uniform types and dosages of nucleating agents are used. Consequently, this section reviews various techniques aimed at reducing the supercooling of salt hydrate PCMs, with an emphasis on heterogeneous nucleation.

Addition of other types of salt hydrates

The lattice-matching method, proposed by Telkes [50] and Lane [51], offers a systematic approach to selecting suitable nucleating agents. According to this method, when the lattice constants of the salt hydrate crystal and the nucleating agent differ by less than 15%, and the nucleating agent’s melting temperature exceeds that of the salt hydrate crystal, the nucleating agents can effectively reduce the supercooling degree of salt hydrates. The effectiveness of salt hydrate nucleating agents largely depends on their affinity for the crystals. High affinity results in a low contact angle and vice versa. Through crystallographic databases, it has been found that certain nucleating agents, such as borax (Na2B4O7·10H2O) and SrCl2·6H2O, are highly effective for specific salt hydrates like Glauber’s salt (Na2SO4·10H2O) and CaCl2·6H2O, respectively, as presented in Table 3. Telkes [50] discovered that incorporating 1.4% Na2B4O7·10H2O prevented the supercooling degree of a supersaturated Glauber salt solution from exceeding 2°C. Similarly, Li et al. [52] achieved a supercooling degree as low as 2.8°C by adding 4 wt.% SrCl2·6H2O.

Table 3

Crystal structures of salt hydrate PCMs and their potential nucleating agents

In the quest to reduce supercooling in salt hydrates, the lattice-matching principle is not the sole criterion for selecting nucleating agents. Researchers have discovered that certain non-isomorphous and non-isotypic salt additives can effectively suppress supercooling in salt hydrates. Employing an empirical approach, Zhang et al. [53] observed that pure Na2S2O3·5H2O failed to crystallize at a phase change temperature of ~48°C, even when the test specimen was cooled to an ambient temperature of ~20°C. However, the addition of 0.08 wt.% sodium pyrophosphate (Na4P2O7) induced solidification at 46.8°C. Similarly, Mao et al. [54,55] determined that Na2HPO4·12H2O was the most effective nucleating agent for CH3COONa·3H2O when compared with Na2HPO4·12H2O, Na2B4O7·10H2O, Na2CO3·10H2O, Na3PO4·12H2O, and Na2SiO3·9H2O. Through this method, they achieved a supercooling degree of ~2°C with the addition of 5 wt.% Na2HPO4·12H2O. Although non-isomorphous and non-isotypic salt hydrates can effectively suppress supercooling, the mechanisms behind their nucleation-promoting effects remain unclear.

Moreover, salt crystals themselves have been shown to aid in reducing supercooling in salt hydrates. Li et al. [56] demonstrated that the inclusion of potassium chloride (KCl) could decrease the supercooling degree of SAT while also lowering the phase change temperature. In their study, when SAT was mixed with 2, 4, and 6 wt.% KCl, the supercooling degree decreased to 9.2, 3.5, and 3.1°C, and the phase change temperatures were lowered to 54, 53, and 52°C, respectively, from the original 58°C. Equation (16) suggests that reducing the melting temperature is a means to inhibit supercooling in salt hydrate PCMs, as it decreases the total Gibbs free energy of nucleation, facilitating crystal nucleation. Therefore, anti-supercooling can also be achieved by adding substances that lower the phase change temperatures of salt hydrates.

Addition of nanomaterials

Table 4 provides an overview of the supercooling characteristics of nanomaterial-modified salt hydrates. It is evident that the supercooling degree can be dramatically reduced, sometimes even to within 0.1°C, through the addition of suitable nanomaterials. However, the mechanism underlying this reduction has not been definitively established, and only a few possible mechanisms are currently proposed.

Table 4

Summary of the supercooling characteristics of nanomaterial-modified salt hydrate PCMs

Li et al. [56] suggested that nano-Al2O3 can serve as numerous nucleation sites, acting as scaffolds for the attachment and growth of CH3COONa·3H2O crystals. This process is illustrated in Figure 10. The surface of nano-Al2O3 carries a negative charge due to hydroxyl groups, which strongly interact with Na+ ions. This interaction increases the number of CH3COO– and H2O molecules adsorbed onto the surface of nano-Al2O3. However, adding excessive nanomaterials can lead to aggregation due to their extremely high specific surface areas. When nanoscale Al2O3 aggregates into non-nanoscale particles, its effectiveness diminishes as a nucleating agent for suppressing supercooling.

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Schematic of the nucleation mechanism of CH3COONa·3H2O on the surface of nano-Al2O3 [56]. Copyright © 2016, Elsevier.

Moreover, Zhang et al. [63] agreed that nanomaterials are more effective nucleating agents than micro-sized materials because their diameters closely match the critical radius of nucleation crystals. Only a small fraction of crystal formation is required to initiate nucleation. This nucleation mechanism aligns with the one depicted in Figure 8B. Furthermore, Cui et al [4,42] observed that the supercooling degree of SAT could be reduced by 1.58°C from 32°C with the addition of 10 wt.% expanded perlite (EP), but significantly further reduced to 1.4°C with the addition of 2 wt.% nano silica (NS). They noted that the contact angles between the liquid PCMs and NS were only 28.0°, as shown in Figure 11, promoting heterogeneous nucleation and further decreasing the degree of supercooling. This is because the free energy of the nucleation barrier in PCMs is reduced by approximately 95%. However, experimental observations of salt hydrate nucleation facilitated by nanomaterials remain limited, and this possibility is mostly theoretical at this stage.

thumbnail Figure 11

Comparison of the anti-supercooling effect of modified CH3COONa·3H2O composites using micro-materials and nano-materials. (A) Contact angle between EP and liquid SAT. (B) Supercooling degree of SAT-10EP. (C) The morphology of EP particles. (D) Contact angle between NS and liquid SAT. (E) Supercooling degree of SAT-2NS. (F) Morphology of NS particles. (G) Possible nucleation mechanism of NS on the crystallization of SAT. Adapted with permission from references [4,42], Copyright © 2023, Elsevier, Copyright © 2022, Elsevier.

Other optimization methods on anti-supercooling

Hydrophilic porous media have proven effective in reducing the supercooling of hydrated salts. The hydrophilic surfaces of porous media facilitate the adsorption of water molecules and salt ions due to capillary action and surface tension. This promotes the heterogeneous nucleation of hydrated salts, as depicted in Figure 12. Yang et al. [64] discovered that when CaCl2·6H2O, CH3COONa·3H2O, and Na2SO4·10H2O were absorbed into diatomite, the supercooling degrees of salt hydrate PCMs were reduced by at least 10, 40, and 10°C, respectively. Similarly, Wang et al. [65] employed three-dimensional (3D) graphene as a carrier to absorb Na2SO4·10H2O, resulting in a decrease of approximately 5°C in the supercooling degree.

thumbnail Figure 12

Effect of porous media on the anti-supercooling of salt hydrate PCMs. (A) Step-cooling curves of diatomite porous media containing CaCl2·6H2O. (B) Step-cooling curves of diatomite porous media containing CH3COONa·3H2O. (C) Step-cooling curves of diatomite porous media containing Na2SO4·10H2O. (D) Comparison of nucleation mechanisms by porous media and nucleating agent. (E) Influence of 3D-rGO porous media on the supercooling degree and the corresponding supercooling degree reduction rate of Na2SO4·10H2O. Adapted with permission from references [64,65], Copyright © 2019,Wiley, Copyright © 2018, Wiley.

Moreover, other methods such as external field control (e.g., magnetic field, ultrasound, mechanical vibration [66], electric field, and microwave) and other techniques (e.g., wire interference and surface tension) can also be used to suppress supercooling. Although Zhao et al. [35] discussed several methods and techniques in a review that piqued researchers’ interest, achieving anti-supercooling solutions for salt hydrate PCMs through controllable external fields remains in the experimental stage and can be expensive.

PHASE SEPARATION

Salt hydrate PCMs exhibit incongruent melting during the endothermic process, leading to phase separation during multiple thermal cycles, as shown in Figure 13. The phase separation, characterized by some of the anhydrous salt settling to the bottom of the container due to gravity, can result in a progressive degradation of the heat-storage capacity of the salt hydrates and a reduction in their service life. Additionally, nucleating agent particles in salt hydrate liquids or solids can deposit and aggregate, exacerbating the issue of supercooling. Therefore, addressing phase separation in salt hydrate PCMs is a pressing concern. This section reviews several empirical measures proposed in the literature to tackle this problem. However, these methods still have some shortcomings and remain a focus of ongoing research.

thumbnail Figure 13

Methodology for inhibition of phase separation of salt hydrate PCMs.

Thickening

Thickening involves adding thickening materials to the salt hydrate liquid to increase its viscosity. This helps reduce the phase-separation rate, improving the uniformity of salt hydrates in solution and enhancing their long-term stability during multiple hydration/dehydration thermal cycles. The mechanisms of thickeners can be summarized as follows: First, the hydrophilic chains of thickeners associate with surrounding water molecules through hydrogen bonds, forming a gel-like structure that increases the system’s viscosity. Second, thickeners swell after absorbing water to form a flocculent substance, which combines with water to create a colloid. However, it is crucial to select the appropriate thickener, as excessive amounts can make sample preparation difficult and lead to the formation of air bubbles, resulting in poor PCM performance.

Table 5 lists different thickeners for different salt hydrate PCMs. Marks [67] found that 9% attapulgite clay could eliminate the segregation of Na2SO4·10H2O and stated that the addition of thickeners effectively delays the decline in the storage capacity of salt hydrate PCM systems. Bao et al. [68] discovered that adding 25 wt.% super-absorbent polymers eliminated the segregation of CaCl2·6H2O. Meanwhile, Shahbaz et al. [69] concluded that 2 wt.% silica fumes could also achieve the same effect, and the salt hydrate PCM composite exhibited good thermal stability after 100 cycles. More recently, Yang et al. [5] eliminated segregation by thickening CH3COONa·3H2O with xanthan gum, and the material showed improved thermal stability after 500 cycles. However, Kumar et al. [22] noted that the effectiveness of thickening depends on the chemical compatibility between the thickener and salt hydrate. Therefore, developing or discovering more effective thickeners is still a research priority.

Table 5

Summary of thickeners for various salt hydrate PCMs

Additionally, Efimova et al. [71] found that while some thickeners are effective in the short term, they may lose their effectiveness when subjected to long-term thermal cycling. As depicted in Figure 14, even with the addition of thickeners like SiO2 and methylcellulose, some inorganic salts may still precipitate during long-term use. To the best of our knowledge, existing literature does not provide evidence that a specific thickener’s performance can guarantee the stability of salt hydrate PCMs after enduring more than 5000 thermal cycles.

thumbnail Figure 14

Ternary salt hydrate specimens [Zn(NO3)2·6H2O/Mn(NO3)2·4H2O/KNO3] with thickening agent SiO2, xanthan, or methylcellulose after 480 freezing/melting cycles [71]. Copyright © 2015, Elsevier.

Consequently, ensuring the long-term stability and reliability of thickeners remains a significant research challenge, as it is crucial for the practical application of salt hydrate PCMs in engineering. Moreover, various measures can be explored to restore the unstable state of salt hydrate PCMs after prolonged operation, drawing inspiration from the self-healing mechanisms observed in materials like concrete [72].

Gelling

Gelling involves the addition of a crosslinking agent to thickened salt hydrates, creating a 3D solid-gel structure, as shown in Figure 15. The PCMs loaded into this network structure can store and release thermal energy during the phase change process, making it an efficient and reliable solution for various applications [4].

thumbnail Figure 15

Schematic of the gelling mechanism of salt hydrate PCMs.

However, research on gelled salt hydrates is relatively limited, and only a few studies have reported on this approach. In 2007, Lan et al. [73] applied gelation technology to confine salt hydrates within a restricted space. They used polymers such as sodium acrylate, sodium alginate, N,N-methylene bisacrylamide, and crosslinking agents like K2S2O8 and Na2SO3. This resulted in the growth of most Na2HPO4·12H2O crystals being less than 0.1 mm, and the latent heat of their salt hydrate PCMs remained constant after 50 thermal cycles. Similarly, Liu et al. [74,75] used carbon nanotubes and graphene oxide as crosslinking agents for acrylate-sodium-based polymers, achieving excellent thermal and chemical stability after 500 thermal cycles. In addition, Karimineghlani et al. [76] discovered that certain thickeners can directly form gels with salt hydrates without requiring crosslinking agents. For instance, polyvinyl alcohol (PVA) as a thickener can be mixed with lithium nitrate trihydrate to create a solid gel due to the crosslinking induced by Li+ ions.

Compared with thickeners, gelled salt hydrates do not flow and possess a consistency similar to jelly-like pastes, often exhibiting mechanical properties to some extent. Recently, using a similar strategy, Cui et al. [3] introduced an innovative TES aggregate based on salt hydrate PCMs. This approach resulted in excellent thermal stability and mechanical strength, leading to desirable thermal and mechanical properties for TES concrete. In summary, gelling is a promising technology for inhibiting phase separation in salt hydrate PCMs, as it can create a more stable matrix for these materials. This advancement represents a significant step toward facilitating the practical application of salt hydrate PCMs.

Porous carriers

Porous materials are commonly employed as supporting materials to contain salt hydrates, mitigating phase separation. This approach capitalizes on the capillary force, Van der Waals force, surface tension, and hydrogen bonds between the salt hydrates and the porous matrixes [77]. Porous materials serve as effective carriers for salt hydrates, as each pore in the porous structure functions as a miniature encapsulator, providing a heterogeneous surface where salt hydrate droplets can be captured. Notably, porous aggregates such as EP [4,78,79], expanded vermiculite [8082], and diatomite [83,84] have been found to be chemically compatible with salt hydrate PCMs, as shown in Figure 16, making them suitable carriers. Notably, to ensure the long-term stability and reliability of salt hydrate PCMs when used in practical engineering applications, coating systems can be employed. These systems effectively encapsulate the porous carriers and their contents, preventing leakage and ensuring the sustained performance of salt hydrate PCMs over multiple thermal cycles. This combination of porous carriers and protective coatings represents a promising solution for various TES applications.

thumbnail Figure 16

Morphologies of different porous carriers and the chemical compatibility between salt hydrate PCMs and porous carriers. (A) SEM image of EP. (B) XRD pattern of EP containing CaCl2·6H2O. (C) Fourier transform infrared spectroscopy (FT-IR) of EP containing CaCl2·6H2O. (D) SEM image of expanded vermiculite. (E) XRD pattern of expanded vermiculite containing Na2SO4·10H2O and Na2CO4·10H2O. (F) FT-IR spectrum of expanded vermiculite containing Na2SO4·10H2O and Na2CO4·10H2O. (G) SEM image of diatomite. (H) XRD pattern of diatomite containing CH3COONa·3H2O. (I) FT-IR spectrum of diatomite containing CH3COONa·3H2O. Adapted with permission from references [78,81,84], Copyright © 2017, Elsevier, Copyright © 2019, Elsevier, Copyright © 2022, Elsevier.

The analysis from Table 6 reveals that the loading capacity of salt hydrates into porous aggregates typically exceeds 50 wt.%, with the specific capacity influenced by the type of salt hydrates due to differences in viscosity. Moreover, the fact that salt hydrate PCMs maintain a high latent heat even after multiple thermal cycles underscores the excellent thermal stability provided by porous aggregates. However, it is crucial to emphasize that porous carriers containing salt hydrates still require additional coating measures before they can be incorporated into cement-based materials. Despite the use of vacuum pressure to immerse salt hydrate PCMs into the porous carrier, there remains a risk of leakage after multiple cycles, which could potentially affect the corrosion of steel reinforcement within structural elements. Essentially, while salt hydrates are contained within the pore structure, they are not fully isolated from the external environment. This allows for an exchange between the internal ions of the salt hydrate and the free water present in the cement-based materials. Therefore, it is necessary to provide external protection to porous carriers containing salt hydrates, and this can be further understood through previous research on coating system strategies for PCMs [85].

Table 6

Summary of porous carriers for various salt hydrate PCMs a

Microencapsulation

Microencapsulation is a valuable technique for addressing the phase separation issues associated with salt hydrate PCMs. This technology involves encapsulating salt hydrates within protective shells, preventing their contact with the external environment and effectively inhibiting phase separation, as depicted in Figure 17. Various microencapsulation methods have been developed for salt hydrate PCMs, including improved interfacial polymerization [86,87], emulsion polymerization [88], water-in-oil (W/O) emulsions [89], and the sol-gel method [90].

thumbnail Figure 17

Microencapsulation technology for salt hydrate PCMs [86]. Copyright © 2020, American Chemical Society.

Table 7 summarizes the research on microencapsulation for salt hydrate PCMs, and provides an overview of research on microencapsulation for salt hydrate PCMs. These studies have demonstrated the successful encapsulation of different salt hydrates using various materials and encapsulation techniques. For instance, tetraethoxysilane was used to synthesize SiO2 shells for encapsulating Na2SO4·10H2O [87,88], and methylmethacrylate and ethyl acrylate were employed to encapsulate Na2HPO4·7H2O [91]. Microencapsulation technology effectively prevents phase segregation by isolating salt hydrates into individual microparticles. However, it is worth noting that microencapsulated salt hydrate PCMs may exhibit lower thermal stability compared with non-encapsulated counterparts, as observed in latent heat capacity after cycling (as discussed in Sections of Thickening and Porous carriers). Organic materials often make up a significant portion of the encapsulation materials, which can limit the improvement of heat transfer in PCMs. Future research in this area may focus on enhancing the mechanical strength of microencapsulated salt hydrate PCMs to better suit engineering applications, especially in scenarios involving complex thermal-mechanical conditions, such as structural function integrated energy storage concrete (Figure 4).

Table 7

Overview of microencapsulation technologies for various salt hydrate PCMs a

Other optimization methods for phase separation

From an application perspective, phase separation, caused by inconsistent melting, can be mitigated by adding excess water to dilute salt hydrates, which is a straightforward and practical method [92]. This approach ensures a uniform distribution of all nearby PCM components to some extent and helps dissolve additional anhydrous salts deposited in the system, maintaining a saturated salt solution. However, a drawback of this method is a reduction in overall energy storage density due to dilution [93]. Additionally, the problems of supercooling and lower thermal conductivity resulting from extra water addition can be addressed using the techniques discussed in Sections of SUPERCOOLING and THERMAL CONDUCTIVITY.

Eutectic compositions are another technique employed to prevent phase separation and improve the thermal cycle stability of salt hydrate PCMs. This approach leads to a more stable structure through the rearrangement of hydrogen bonds [94]. For instance, a study by Zheng et al. [95] investigated PCMs with a mass ratio of 9:1 (Na2HPO4·12H2O and Na2SO4·10H2O) to achieve improved thermal cycle stability.

THERMAL CONDUCTIVITY

Enhancing the thermal conductivity of PCMs is critical in improving their performance for TES applications. The existing literature provides various techniques for strengthening thermal transfer efficiency, ranging from macroscopic methods like fins to microscopic ones involving nanoparticles [22]. One way to assess thermal conductivity enhancement is by measuring the thermal conductivity of solid or liquid salt hydrate PCMs. High thermal conductivity can be achieved in PCMs by introducing various additives with different dimensional properties (0D, 1D, 2D, and 3D), as illustrated in Figure 18. These additives typically have significantly higher thermal conductivity than salt hydrate PCMs, which usually have thermal conductivities in the range of 0.5 to 1.5 W/(m K) [22,96], as shown in Table 8.

thumbnail Figure 18

Methodology of thermal conductivity enhancement for salt hydrate PCMs.

Table 8

Summary of additives used to enhance thermal conductivity in salt hydrate PCMs [96106]

Mechanism for thermal conduction enhancement

Heat transfer generally occurs through conduction, convection, or radiation, as illustrated in Figure 19A. Thermal conduction is the primary mode of heat transfer in solid materials, described by Eq. (20), which is derived from Fourier’s law.

q = K T , (20)

where q, K, and T represent the heat flow rate through a unit area per unit time, thermal conductivity, and the local temperature gradient, respectively.

The thermal conductivity of PCMs is influenced by various factors. Among them, phonon scattering is a critical factor that limits the thermal conductivity of PCMs. Phonons, which are quantized lattice vibrations, are responsible for heat transfer within materials. The thermal conductivity carried by phonons can be described using the Debye equation (Eq. (21) [107109]) and Eq. (22), as depicted in Figure 19B.

thumbnail Figure 19

Mechanism of thermal conduction and enhancement in PCMs. (A) Schematic illustration of three basic heat transfer modes [110]. Copyright © 2019, Wiley. (B) Phonon thermal conductivity and related components [98]. Copyright © 2020, Elsevier. (C) Schematic illustration of heat transfer mechanism of PCMs enhanced by additives (modified by Reference [105]). Copyright © 2021, Elsevier.

K = 1 3 C v ( ω ) v ( ω ) l ( ω ) d ω , (21)

v = ω ( k ) / k , (22)

where Cv , v, and l denote the specific heat capacity per volume, phonon group velocity, and mean free path of phonons in a material, respectively; ω and k denote the lattice vibration frequency and wavevector, respectively. The low phonon velocity and short mean free path contribute to the relatively low thermal conductivity of PCMs to some extent [105]. To enhance the thermal conductivity of PCMs, it is effective to incorporate additives with high thermal conductivity and thermal transfer efficiency. This strategy creates pathways or networks for heat transfer within the PCMs, as illustrated in Figure 19C.

Enhancing the thermal conductivity of salt hydrate PCMs

As depicted in Table 9, Cui et al. [57] conducted a study demonstrating that the incorporation of 0.5 wt.% nano copper (a 0D additive) into CH3COONa·3H2O resulted in a notable improvement in thermal conductivity, achieving an increase of 25.1%. In another study by Xiao et al. [111], copper foam (considered a 3D additive) was explored as a potential thermal conductivity enhancer. They found copper foam to be advantageous due to its ability to establish a continuous 3D structure that facilitates phonon propagation [112]. Consequently, when CH3COONa·3H2O was combined with copper foam, the thermal conductivity exhibited a remarkable increase of 176.3%.

Table 9

Comparison of thermal conductivity of salt hydrate PCMs before and after optimization with high-thermal-conductivity additives

Nevertheless, the inclusion of copper, a metal-based material, in salt hydrates comes with a significant risk of corrosion. Hence, researchers have focused on carbon-based and ceramic-based materials, which offer the dual advantages of high thermal conductivity and chemical inertness as thermal conductivity enhancers. These materials come in various dimensional forms. Among the 2D additives, such as graphene nanoplatelets [5], expanded graphite [120], and graphite flakes [113], expanded graphite displayed the optimal effects among them, as highlighted in Table 9. When 12 wt.% expanded graphite was introduced, the thermal conductivity saw a remarkable improvement to 6.4 W/(m K), constituting a 1225% increase. However, it is essential to note that expanded graphite is hydrophobic and does not adsorb salt hydrates in the same manner as organic PCMs. Consequently, the large particle size of expanded graphite limits the volumetric heat storage capacity. On the other hand, for ceramic-based materials, Cui et al. [42] recently developed an innovative SAT composite using SiC foam (a 3D additive) as the thermal conductivity enhancer. They also revealed the enhancement mechanism of 3D additives on the thermal conductivity of salt hydrate PCMs through microthermal infrared imaging, as depicted in Figure 20.

thumbnail Figure 20

Enhancing the thermal conductivity of salt hydrate PCMs using three-dimensional additive. (A) Schematic of the enhancement mechanism and (B) thermal infrared imaging of the corresponding heat transfer process.

Moreover, rather than relying solely on individual additives, researchers have discovered that the thermal conductivity of salt hydrate PCMs can be further enhanced by combining additives of different dimensions, harnessing synergistic effects. A notable example is the collaborative effort by Yang et al. [5], who employed carbon nanotubes (1D additive) along with carbon fiber (1D additive), expanded graphite (2D additive), and graphene nanoplates (2D additive) to boost the thermal conductivity and photothermal charging efficiency of CH3COONa·3H2O, as illustrated in Figure 21. In their research, the thermal conductivity of salt hydrate PCMs improved by 54.9%, while the photothermal conversion efficiency surged to 89.3% upon the incorporation of graphene nanoplates (2D additive) into the salt hydrate PCMs/carbon nanotubes (1D additive) composite, rendering it highly proficient in solar energy capture.

thumbnail Figure 21

Enhancement of thermal conductivity through synergistic usage of carbon nanotube (1D additive) with carbon fiber (1D additive), expanded graphite (2D additive), and graphene nanoplates (2D additive). (A) Thermal conductivity enhancement by carbon nanotube and carbon fiber. (B) Thermal conductivity enhancement by carbon nanotube and expanded graphite. (C) Thermal conductivity enhancement by carbon nanotube and graphene nanoplates. Besides, SEM images of PCMs modified by different dimensions of carbon-based additives are shown in: (D) SAT-S-2MWCNTs-1.5CF 100 × and (G) 5000 ×, (E) SAT-S-2MWCNTs-1.5 EG 500 × and (H) 5000 ×, and (F) SAT-S-2MWCNTs-1.5GNPs 500 × and (I) 5000 × [5]. Copyright © 2022, Elsevier.

PHASE CHANGE TEMPERATURE

Phase change temperature is a critical factor in the design of PCM-enhanced building energy storage systems. These systems are expected to regulate heat on a diurnal scale, respond to short-term fluctuations like peak-valley electricity rates, and provide thermal or cooling energy over longer periods, accommodating seasonal variations in solar radiation and regional cold supply. As a result, PCMs must be tailored to meet the diverse temperature requirements outlined in Section of PCMs-ENHANCED BUILDING ENERGY STORAGE SYSTEMs.

To address these varying demands, binary mixtures, such as salt hydrates combined with organics or inorganic salts and ternary mixtures, are commonly employed to design and adjust PCMs with different phase change temperatures, as detailed in Table 10. For instance, in pursuit of a suitable PCM for air-conditioning cold storage, Zou et al. [123] introduced urea as a temperature-regulating agent. Their research demonstrated that the phase change temperature of CaCl2·6H2O could be modulated, shifting from 9.5 to 29°C. They attributed this temperature adjustment to the presence of urea-generated amino groups, which weaken the interaction forces between CaCl2 molecules and H2O molecules, ultimately leading to a reduction in the phase change temperature. However, it is essential to note that not all temperature-regulating agents are universally compatible with all PCMs. As exemplified in Figure 22A. Fu et al. [124] reported unsatisfactory results when utilizing urea with CH3COONa·3H2O. The addition of urea resulted in the formation of two melting peaks and a significant reduction in the latent heat of CH3COONa·3H2O when urea content exceeded 11%. Such alterations are undesirable in practical engineering applications. In light of these challenges, Yang et al. [5] introduced a novel temperature regulator, NHCl4, into CH3COONa·3H2O. Their research showed that NH4Cl could effectively tailor the phase change temperature of CH3COONa·3H2O, ranging from 57.5 to 45.1°C, making it adaptable to different application scenarios, as depicted in Figure 22B. However, it is crucial to exercise caution when employing NH4Cl due to the potential adverse effects of its volatilized gas on human health.

thumbnail Figure 22

Differential scanning calorimetry curves of CH3COONa·3H2O with different temperature regulators. (A) Urea [124] and (B) NHCl4 [5]. Copyright © 2018, Elsevier, Copyright © 2022, Elsevier.

Table 10

Summary of temperature-regulated agents for virous salt hydrate PCMs

Nonetheless, adjusting the melting point of salt hydrate PCMs through the use of temperature-regulating agents can also lead to a reduction in latent heat, as evident from the data presented in Table 10. Furthermore, the impact of varying agent contents can yield notably distinct outcomes even for identical salt hydrates. Therefore, in future endeavors involving the design of salt hydrate PCM-enhanced building energy storage systems, a critical consideration must be to ensure the preservation of a substantial latent heat capacity even when modifying the phase change temperature using these agents.

In addition to NH4Cl, other potential temperature-regulating agents have been explored in the quest to tailor PCM phase change temperatures. Notably, Li et al. [56] introduced KCl as a candidate temperature-regulating agent. Their research, based on density functional theory calculations, revealed that K+ ions could interact with CH3COO ions by forming contact-ion pairs, weakening the interactions between anhydrous salts and water molecules, and thus reducing the phase change temperature [56,125]. However, it is important to note that the phase change temperature remained relatively constant when the KCl content exceeded 8 wt.%. Unfortunately, the lowest phase change temperature achieved for the SAT/KCl composite was 55°C, which was unsuitable for centralized energy storage systems. To address this issue, Li et al. [12] employed a ternary mixing approach. They incorporated an additional 3% urea into the mix, substantially reducing the phase-transition temperature of the binary SAT and KCl combination. This adjustment yielded a favorable phase change temperature of 47.8°C and a higher latent heat of 242.0 J/g.

Furthermore, another technique known as the eutectic salt method involves adding a certain proportion of another hydrated salt to the base hydrated salt to create a eutectic hydrated salt, effectively altering the melting point. Rao et al. [79] and Xie et al. [81] showcased the efficacy of this method in crafting salt hydrates with distinct phase change temperatures. For instance, when the ratio of Na2SO4·10H2O to Na2CO3·10H2O was adjusted to 1:1, the resulting eutectic salt hydrate displayed a phase-transition temperature of approximately 26°C. This value was lower than that of both individual salt hydrates, making it suitable for passive-construction thermal storage systems, such as thermoregulated wall and floor components, as illustrated in Figure 4.

CORROSION TO METALS

Metal materials are often favored for macro-encapsulation of PCMs due to their desirable properties, including resistance to wear, high thermal conductivity, ductility, and overall durability. However, the issue of corrosion poses a significant challenge to the safe and cost-effective application of TES systems involving most salt hydrates [92]. This is primarily because metal materials tend to corrode upon contact with salt hydrates, effectively serving as an electrolyte solution. Consequently, various techniques, such as gravimetric analysis and microscopic observation, as well as industry standards (ASTM G1–03) [130132], have been developed to calculate the corrosion rate (CR, calculated by Eqs. (23) and (24)) of metal materials. Additionally, classification guidelines have been established to provide clear guidance, as outlined in Table 11. In practical applications, metal materials must exhibit corrosion resistance, with the CR being less than 9.9 mg/(cm2 a).

Table 11

Industry standard for corrosion weight loss measurement guideline [130132]

m = m ( t 0 ) m ( t ) , (23)

CR = m / A c ( t 0 t ) , (24)

where Δm, m(t 0), and m(t) denote the mass loss, initial mass, and mass measured at a specific time, respectively; A c denotes the area in cm2, and t 0 and t are the initial and related times, respectively.

Table 12 overviews the different metal materials employed with various salt hydrates. For instance, Calabrese et al. [133] noted that copper and aluminum alloy surfaces displayed varying degrees of degradation after 7 days of corrosion in Mg(NO3)2·6H2O liquid. Copper alloy surfaces exhibited numerous Cu(NO3)2 crystal corrosion products, while aluminum alloy surfaces showed minimal signs of corrosion, featuring only a thin Al2O3 layer (commonly referred to as a passivation film), as illustrated in Figure 23. As a result, they concluded that aluminum alloy, in comparison to copper alloys, is a more suitable and effective material for coating Mg(NO3)2·6H2O containers. Subsequently, Honcova et al. [134] corroborated these findings, reporting a CR of 2.3 mg/(cm2 a) for aluminum alloy in Mg(NO3)2·6H2O liquid, which falls well below the industry standard of 9.9 mg/(cm2 a).

thumbnail Figure 23

SEM images of the corroded surface of (A) copper alloy and (B) aluminum alloy after 7 days’ corrosion in Mg(NO3)2·6H2O at 120°C [133]. Copyright © 2019, Elsevier.

Table 12

Corrosion performance of metals for long-term encapsulation of various salt hydrate PCMs

Moreover, according to research conducted by Devanuri et al. [138], stainless steel demonstrates remarkable resistance to corrosion from virtually all hydrated inorganic salts. This exceptional resistance is attributed to the presence of 15% chromium in stainless steel. Chromium, compared with other elements, has a superior ability to form an oxide (passivation) film. This film acts as a protective barrier, effectively isolating the metal from external inorganic salts and preventing further corrosion. In the event of damage, chromium can regenerate this protective passivation film, ensuring long-term durability. As a result, stainless steel plays a crucial role in enhancing the corrosion resistance of salt hydrates. However, Cabeza et al. [139,140] caution against the indiscriminate use of stainless steel for long-term encapsulation of hydrated chloride. While no corrosion was observed during their testing period, stainless steel remained at a high risk of contact with chloride ions. Specifically, stainless steel may accelerate corrosion due to the unique characteristics of chloride ions, such as their small ion radius and strong penetration ability. These ions can preferentially adsorb onto the passivated iron carbonate film, leading to pitting, stress, and crevice corrosion. The volume deformation of the PCMs, occurring before and after the phase change, can also influence the shape of the container, exacerbating its deterioration. Therefore, evaluating strip specimens alone may not provide a complete picture. Metal materials must be configured into container shapes to accurately assess whether the metal container’s deformation affects its CR. Because existing investigations rely on laboratory test methods, studies have been scarce monitoring the practical application of stainless steel with salt hydrates over the past decades. Consequently, stainless steel has not been widely adopted for encapsulating salt hydrates. Long-term studies using practical measurements are imperative in the future to gather more reliable data.

Additionally, various measures can be implemented to mitigate corrosion and meet specific application requirements. The sacrificial anode strategy [141], commonly employed in engineering applications to prevent steel bar corrosion in bridge columns, can also be applied in this context. Furthermore, galvanizing the metal surface represents another effective approach. Coating a non-metallic protective or barrier layer on the metal surface is an excellent choice for isolating the metal from salt hydrates. However, it is noteworthy that, to date, researchers have not extensively explored the impact of salt hydrates on the corrosion resistance of various metal surface modifications.

APPLICATIONS OF SALT HYDRATE PCMS FOR BUILDING

The application of salt hydrates as PCMs for building energy storage systems can be divided into three categories, including PCMs-enhanced facilities, PCMs-enhanced building envelopes, and PCMs-enhanced geostructures. These applications are envisioned to facilitate diurnal heat regulation in the short term and provide thermal energy or cold energy distribution over the course of months or even seasons in the long term.

Facilities

Building facilities primarily encompass heating, ventilating, and air conditioning systems, often abbreviated as HVAC. Farid et al. [142] categorize PCMs into materials for storage of coolness in air conditioning applications (T m < 15°C), materials for absorption refrigeration (T m > 90°C), and materials for solar heating and related applications (15°C < T m < 90°C). Zeinelabdein et al. [128] reviewed various free cooling technologies for ventilating and air conditioning systems, highlighting the promising sustainability of using PCMs to minimize energy consumption. They emphasized the potential of night cooling strategies employing PCMs to effectively maintain indoor temperatures within the comfort zone while substantially reducing cooling loads across a range of climates. Moreover, for heating systems, the temperature characteristics of salt hydrate PCMs lend themselves to a variety of applications. These include solar water heating [143145], solar drying [16,146,147], photothermal /photovoltaic systems [148,149], waste heat recovery [150], and other related fields.

Notably, as depicted in Figure 24A, solar water heating systems are particularly favored in regions with temperate, arid, and tropical climates. These systems can be categorized as PCM-enhanced integrated and PCM-enhanced non-integrated systems [145]. In non-integrated solar collectors, the separation of PCM mass from the solar collector provides greater design flexibility, allowing for increased PCM utilization and compatibility with various external systems. For instance, Kılıçkap et al. [144] integrated salt hydrate PCMs with a hot water collector and conducted tests in Turkey. In their investigation, the hot water collector containing CaCl2·6H2O exhibited the highest heat collection efficiency, extending the availability of hot water at the desired temperature by 1–1.5 h. Additionally, Ding et al. [143] assessed the power-saving and heat loss reduction rates in solar water heating systems, both with and without PCMs, across six cities in China (Lhasa, Kunming, Shenyang, Zhengzhou, Changsha, and Guangzhou). Their findings indicated that Lhasa exhibited the highest power-saving rate, while Guangzhou demonstrated the most significant heat loss reduction rate.

Moreover, the drying of agricultural products is emerging as a new trend in PCM applications, particularly when moderate and consistent temperatures are required during the drying process [16]. Drying processes are known to be energy-intensive within the food industry. Recent research by Madhankumar et al. [146] combined solar drying devices with PCMs to efficiently dry agricultural products using solar energy, as shown in Figure 24B. Their study revealed that PCMs equipped with fins substantially reduced specific energy consumption, accelerated moisture drying, and yielded robust, high-quality agricultural products.

thumbnail Figure 24

Applications of salt hydrate PCMs in solar energy storage and utilization. (A) Solar water heating, adapted with permission from references [143145], Copyright © 2020, Elsevier, Copyright © 2018, Elsevier, Copyright © 2021, Elsevier, and (B) solar drying, adapted with permission from references [16,146,147], Copyright © 2014, Elsevier, Copyright © 2023, Elsevier, Copyright © 2021, Elsevier.

Building envelopes

The integration of PCMs into the building envelope helps with building thermal management (e.g., peak heat flux reduction and time delay) as well as in reducing building energy consumption, which stands out as a promising approach. This innovation enables the regulation of room temperatures, maintaining them within the thermal comfort range of 20–28°C, and facilitates the harnessing of solar energy (with the capability to meet hot water demand in the range of 29–68°C) within buildings.

A comprehensive long-term real-size study was conducted by Sonnick et al. [151] to investigate the impact of a salt-hydrate mixture comprising CaCl2·6H2O and MgCl·6H2O on the thermal performance of a lightweight building, utilizing a prefabricated wooden house as a representative model, as shown in Figure 25A. The results demonstrated that, in comparison to a reference room, the building enhanced with PCMs exhibited a remarkable 57% reduction in overall temperature fluctuations and a substantial 62% reduction in day-night temperature swings. Additionally, Bao et al. [68] employed numerical analysis techniques to simulate the indoor temperature variations within building envelopes in Hong Kong and Changsha, applying modified CaCl2·6H2O salt hydrate PCMs. As shown in Figure 25B, their findings underscored the efficacy of PCMs in effectively moderating indoor temperatures, contributing to more energy-efficient and comfortable building environments.

thumbnail Figure 25

Applications of salt hydrate PCMs in building envelopes. (A) A long-term real size experiment using salt hydrate PCMs [151,152], Copyright © 2020, Wiley, Copyright © 2018, Elsevier. (B) Numerical simulation of house integrated with salt hydrate PCMs [68], Copyright © 2020, Elsevier.

Besides, de Gracia et al. [153] employed the life cycle assessment methodology to scrutinize the environmental impact of PCM usage, comparing organic PCMs with salt hydrate PCMs in Mediterranean constructions, as depicted in Figure 26A. The results indicate that the utilization of salt hydrate PCMs reduces the environmental impact associated with manufacturing and allows for a shorter-term payback compared with organic PCMs, with payback times of 25 and 61 years for salt hydrate PCMs and organic PCMs, respectively. Additionally, Mukhamet et al. [154] conducted a comprehensive evaluation of PCMs for building envelope applications, utilizing a multi-criteria decision-making approach, as shown in Figure 26B. In their study, the total annual energy savings of commercial salt hydrate PCMs S27 far exceeded that of other PCMs. And the S27 used in Bamako has an energy saving of approximately 8392 kWh and a 43% reduction in energy consumption. They then ranked various PCMs, including salt hydrate PCMs, organic PCMs, and biobased PCMs, using the Fuzzy AHP-Modified Fuzzy TOPSIS method. Factors considered in the evaluation encompassed thermophysical (thermal conductivity, latent heat of fusion, phase change temperature, specific heat, density, cycling stability, supercooling), economic (initial cost), chemical (toxicity, flammability, corrosiveness), and environmental (recyclability, embodied energy) aspects. According to their study, salt hydrate PCMs are more suitable for savanna climate buildings than organic and biobased PCMs due to high energy savings, low cost, non-flammability, high latent heat energy, and their consistently high-ranking position in the sensitivity analysis.

thumbnail Figure 26

Comparative study of organic PCMs and salt hydrate PCMs applied in building envelopes. (A) The life Cycle Assessment [153] (PCM1 and PCM2 denote organic PCMs and salt hydrate PCMs, respectively), Copyright © 2010, Elsevier. (B) The multi-objective ranking via Fuzzy AHP-Modified Fuzzy TOPSIS method [154] (S and SP both denote salt hydrate PCMs; A and RT both denote organic PCMs; PT denotes biobased PCMs), Copyright © 2021, Elsevier.

Geostructures

Shallow geothermal energy stands as a sustainable and eco-friendly resource that can effectively power heating and cooling systems within buildings. The integration of ground source heat pumps (GSHP) with geostructures, such as energy tunnels [155], energy pile [156], and energy diaphragm wall [157], has emerged as a practical solution. Recently, the incorporation of PCMs into these structures to enhance heat storage density has gained prominence, as illustrated in Table 13.

Table 13

Summary of energy geostructures integrated with PCMs

Alavy et al. [158] developed a thermal caisson by integrating PCMs into energy piles, investigating their impact on the COP of the heat pump system. Results showed that combining PCMs with energy piles improved GSHP system performance by up to 16%, while, without the need for additional drilling, they reduced capital costs by up to 49%. In another study [159], the authors evaluated the influence of PCMs and ordinary backfill materials on the heat transfer performance of precast high-strength concrete energy piles. They suggested that PCMs with a larger latent heat, higher thermal conductivity, and lower melting temperature (under the cooling mode) can enhance the heat transfer performance of energy piles. Furthermore, Mousa et al. [160] explored the feasibility of using PCMs as a thermal storage system in energy piles. Their study recommended partitioning the PCM into smaller containers, noting that while adding PCMs as a whole increased the COP of the heat pump in the energy pile by approximately 5.28%, further partitioning the PCMs into smaller containers raised the COP by about 26%.

Recently, the TES concrete [4,7,169171], renowned for its high heat storage density achieved through the effective integration of concrete and PCMs, has begun to establish itself in the realm of energy geostructures. In this energy pile system, PCMs are divided into small units, and the encapsulated PCM is uniformly distributed in the pile body as coarse aggregate. Cui’s group [161] conducted a comparative analysis of the thermo-mechanical performance of an ordinary pile and a PCM energy pile in saturated sand. Their study revealed that the strain of the PCMs energy pile was 2% smaller than that of the ordinary energy pile, and the displacement was reduced by 6%, effectively enhancing the durability of the energy pile. Furthermore, Bao et al. [8] investigated the thermal response of a PCM energy pile in unsaturated clay. The results indicated that, compared with the traditional energy pile, the temperature of the PCM energy pile is more uniform, and the heat transfer power of the PCM energy pile is higher. Although research on the combination of PCMs and energy geostructures is flourishing, the exploration of salt hydrate PCMs in energy geostructure lags behind that of organic PCMs, with only a few scholars [166,167] participating.

CONCLUSIONS AND RECOMMENDATIONS

This review provided a comprehensive overview of the progress and challenges associated with salt hydrate PCMs in enhancing building energy storage systems. Through critical analysis, this review identified several key issues concerning salt hydrates and explored optimization methods and underlying mechanisms. The following conclusions have been drawn.

(1) Salt hydrates, with their inherent advantages such as non-flammability, high enthalpy, and cost-effectiveness, hold promising prospects for applications in energy storage systems within the construction sector. While solutions to common challenges like supercooling, phase separation, and low thermal conductivity are emerging, further research is essential. Notably, the adoption of salt hydrates in practical applications still lags behind that of organic PCMs.

(2) Nanomaterials represent a potential solution to mitigating supercooling in salt hydrates. Their nanoscale size closely aligns with the critical nucleation radius, significantly reducing the heterogeneous nucleation barrier. However, widespread production of nanomaterial-modified salt hydrates may present challenges due to the need for ultrasonic dispersion and relatively high costs. Future research should focus on exploring efficient methods for supercooling inhibition.

(3) Various technologies, including thickening, gelling, porous-carrier absorption, and microencapsulation, have proven effective in preventing phase separation of salt hydrates. Nevertheless, there is a need for long-term cycle stability assessments and a deeper understanding of the underlying mechanisms, particularly for microencapsulation. In the future, innovative solutions with self-healing capabilities should be developed to address stability issues after multiple cycles. Furthermore, the use of porous carriers for salt hydrate absorption presents a straightforward and efficient method for overcoming phase separation. Consequently, research into developing porous supports with high thermal conductivity and porosity to accommodate salt hydrates is poised to become a prominent area of study.

(4) 3D thermal enhancers have demonstrated a remarkable ability to enhance the thermal conductivity of salt hydrates, outperforming their 2D, 1D, and 0D counterparts. Future research should explore the synergistic use of enhancers with different dimensions to develop salt hydrates with even higher thermal conductivity. Leveraging machine learning techniques can prove instrumental in predicting variations in the phase change temperature of salt hydrates and facilitating the design of salt hydrates with specific phase change temperatures.

(5) The phase change temperature of salt hydrate PCMs can be fine-tuned by incorporating temperature-regulated agents, such as organic materials, other types of salts, or salt hydrates. This adjustment widens the application range of salt hydrate PCMs across diverse fields. However, it is imperative to note that the introduction of temperature regulators often results in a reduction of latent heat capacity. In future designs of salt hydrate PCMs-enhanced building energy storage systems, ensuring substantial latent heat capacity while adjusting the phase change temperature is essential.

In conclusion, salt hydrate PCMs hold great promise for revolutionizing building energy storage systems. To fully harness their potential, continued research, innovation, and practical applications are vital. Addressing the identified challenges and further optimizing these remarkable materials will drive the advancement of sustainable and energy-efficient building solutions.

Data availability

The original data are available from the corresponding authors upon reasonable request.

Funding

This work was supported by the National Natural Science Foundation of China (51925804 and 52208275) and the China Postdoctoral Science Special Foundation (2023T160433).

Author contributions

H.Y. and Y.Z. collated and summarized the literature and wrote the manuscript. H.C. guided the manuscript. All authors discussed and commented on the manuscript.

Conflict of interest

The authors declare no conflict of interest.

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All Tables

Table 1

Comparison between organic PCMs and salt hydrate PCMs

Table 2

Types of low-temperature salt hydrate PCMs (below 120°C) a [1820]

Table 3

Crystal structures of salt hydrate PCMs and their potential nucleating agents

Table 4

Summary of the supercooling characteristics of nanomaterial-modified salt hydrate PCMs

Table 5

Summary of thickeners for various salt hydrate PCMs

Table 6

Summary of porous carriers for various salt hydrate PCMs a

Table 7

Overview of microencapsulation technologies for various salt hydrate PCMs a

Table 8

Summary of additives used to enhance thermal conductivity in salt hydrate PCMs [96106]

Table 9

Comparison of thermal conductivity of salt hydrate PCMs before and after optimization with high-thermal-conductivity additives

Table 10

Summary of temperature-regulated agents for virous salt hydrate PCMs

Table 11

Industry standard for corrosion weight loss measurement guideline [130132]

Table 12

Corrosion performance of metals for long-term encapsulation of various salt hydrate PCMs

Table 13

Summary of energy geostructures integrated with PCMs

All Figures

thumbnail Figure 1

Thermal energy demand in China. (A) Annual heating intensity in north urban China in 2020 [1]. Copyright © 2023, Springer Nature Limited. (B) Historical CO2 emissions from centralized heating at the national level [2]. Copyright © 2023, Elsevier. (C) Residential end-use CO2 emissions in urban areas [3]. Copyright © 2023, Elsevier.

In the text
thumbnail Figure 2

Investigation of PCM applications in buildings. (A) Cluster analysis graph depicting the keywords “reduce building energy consumption” and “material” using VOS viewer. (B) Number of publications on the keyword “phase change material” from 2000 to 2023 (data as of September 2023 from Web of Science). (C) Schematic diagram illustrating the relationship between heat gain and building heat demand.

In the text
thumbnail Figure 3

Classifications of PCMs.

In the text
thumbnail Figure 4

Schematic of various PCMs-enhanced energy storage systems in buildings. (A) PCMs-enhanced centralized thermal/cold storage systems. (B) PCMs-enhanced solar harvesting/heat pump energy storage systems. (C) PCMs-enhanced photothermal energy storage wall/roof structures. (D) PCMs-enhanced thermoregulated wall/floor components. (E) PCMs-enhanced energy piles and (F) PCMs-enhanced energy tunnels. Adapted with permission from refs. [4,5,711], Copyright © 2023, Elsevier, Copyright © 2022, Elsevier, Copyright © 2022, Elsevier, Copyright © 2022, Elsevier, Copyright © 2022, Elsevier, Copyright © 2018, Elsevier, Copyright © 2019, Elsevier.

In the text
thumbnail Figure 5

Challenges of utilizing salt hydrate PCMs in buildings.

In the text
thumbnail Figure 6

Schematic illustration of nucleation mechanisms of salt hydrate PCMs. (A) Schematic of temperature vs. time curve measured by T-history method and (B) nucleation methods to promote the crystallization of salt hydrate PCMs.

In the text
thumbnail Figure 7

Variation of Gibbs free energy for a transition from the liquid state to solid state. (A) Relationship between the nucleation radius and Gibbs free energy. (B) Relationship between the temperature and Gibbs free energy. (C) Labile-cluster model of hydrate nucleation [37]. Copyright © 2020, Royal Society of Chemistry. Note: ΔG denotes the Gibbs free energy; ΔG(r c) denotes the Gibbs free energy corresponding to the critical radius; Δg and ΔT denotes the difference in free energy per unit volume and supercooling degree of PCMs, respectively.

In the text
thumbnail Figure 8

Schematic of the contact angle between the crystal nucleus, liquid medium, and substrate surfaces for different structures. (A) The nucleus growing on the surface of a flat substrate [42]. Copyright © 2022, Elsevier. (B) The nucleus growing on the substrate surface under different structures for identical nucleation radii and contact angles.

In the text
thumbnail Figure 9

Effect of cooling rate. (A) Supercooling degree as a function of cooling rate (the dashed lines give the linear trends of the data) [47]. Copyright © 2016, Elsevier. (B) DSC analysis of commercial PCM for different cooling rates [48]. Copyright © 2013, Elsevier.

In the text
thumbnail Figure 10

Schematic of the nucleation mechanism of CH3COONa·3H2O on the surface of nano-Al2O3 [56]. Copyright © 2016, Elsevier.

In the text
thumbnail Figure 11

Comparison of the anti-supercooling effect of modified CH3COONa·3H2O composites using micro-materials and nano-materials. (A) Contact angle between EP and liquid SAT. (B) Supercooling degree of SAT-10EP. (C) The morphology of EP particles. (D) Contact angle between NS and liquid SAT. (E) Supercooling degree of SAT-2NS. (F) Morphology of NS particles. (G) Possible nucleation mechanism of NS on the crystallization of SAT. Adapted with permission from references [4,42], Copyright © 2023, Elsevier, Copyright © 2022, Elsevier.

In the text
thumbnail Figure 12

Effect of porous media on the anti-supercooling of salt hydrate PCMs. (A) Step-cooling curves of diatomite porous media containing CaCl2·6H2O. (B) Step-cooling curves of diatomite porous media containing CH3COONa·3H2O. (C) Step-cooling curves of diatomite porous media containing Na2SO4·10H2O. (D) Comparison of nucleation mechanisms by porous media and nucleating agent. (E) Influence of 3D-rGO porous media on the supercooling degree and the corresponding supercooling degree reduction rate of Na2SO4·10H2O. Adapted with permission from references [64,65], Copyright © 2019,Wiley, Copyright © 2018, Wiley.

In the text
thumbnail Figure 13

Methodology for inhibition of phase separation of salt hydrate PCMs.

In the text
thumbnail Figure 14

Ternary salt hydrate specimens [Zn(NO3)2·6H2O/Mn(NO3)2·4H2O/KNO3] with thickening agent SiO2, xanthan, or methylcellulose after 480 freezing/melting cycles [71]. Copyright © 2015, Elsevier.

In the text
thumbnail Figure 15

Schematic of the gelling mechanism of salt hydrate PCMs.

In the text
thumbnail Figure 16

Morphologies of different porous carriers and the chemical compatibility between salt hydrate PCMs and porous carriers. (A) SEM image of EP. (B) XRD pattern of EP containing CaCl2·6H2O. (C) Fourier transform infrared spectroscopy (FT-IR) of EP containing CaCl2·6H2O. (D) SEM image of expanded vermiculite. (E) XRD pattern of expanded vermiculite containing Na2SO4·10H2O and Na2CO4·10H2O. (F) FT-IR spectrum of expanded vermiculite containing Na2SO4·10H2O and Na2CO4·10H2O. (G) SEM image of diatomite. (H) XRD pattern of diatomite containing CH3COONa·3H2O. (I) FT-IR spectrum of diatomite containing CH3COONa·3H2O. Adapted with permission from references [78,81,84], Copyright © 2017, Elsevier, Copyright © 2019, Elsevier, Copyright © 2022, Elsevier.

In the text
thumbnail Figure 17

Microencapsulation technology for salt hydrate PCMs [86]. Copyright © 2020, American Chemical Society.

In the text
thumbnail Figure 18

Methodology of thermal conductivity enhancement for salt hydrate PCMs.

In the text
thumbnail Figure 19

Mechanism of thermal conduction and enhancement in PCMs. (A) Schematic illustration of three basic heat transfer modes [110]. Copyright © 2019, Wiley. (B) Phonon thermal conductivity and related components [98]. Copyright © 2020, Elsevier. (C) Schematic illustration of heat transfer mechanism of PCMs enhanced by additives (modified by Reference [105]). Copyright © 2021, Elsevier.

In the text
thumbnail Figure 20

Enhancing the thermal conductivity of salt hydrate PCMs using three-dimensional additive. (A) Schematic of the enhancement mechanism and (B) thermal infrared imaging of the corresponding heat transfer process.

In the text
thumbnail Figure 21

Enhancement of thermal conductivity through synergistic usage of carbon nanotube (1D additive) with carbon fiber (1D additive), expanded graphite (2D additive), and graphene nanoplates (2D additive). (A) Thermal conductivity enhancement by carbon nanotube and carbon fiber. (B) Thermal conductivity enhancement by carbon nanotube and expanded graphite. (C) Thermal conductivity enhancement by carbon nanotube and graphene nanoplates. Besides, SEM images of PCMs modified by different dimensions of carbon-based additives are shown in: (D) SAT-S-2MWCNTs-1.5CF 100 × and (G) 5000 ×, (E) SAT-S-2MWCNTs-1.5 EG 500 × and (H) 5000 ×, and (F) SAT-S-2MWCNTs-1.5GNPs 500 × and (I) 5000 × [5]. Copyright © 2022, Elsevier.

In the text
thumbnail Figure 22

Differential scanning calorimetry curves of CH3COONa·3H2O with different temperature regulators. (A) Urea [124] and (B) NHCl4 [5]. Copyright © 2018, Elsevier, Copyright © 2022, Elsevier.

In the text
thumbnail Figure 23

SEM images of the corroded surface of (A) copper alloy and (B) aluminum alloy after 7 days’ corrosion in Mg(NO3)2·6H2O at 120°C [133]. Copyright © 2019, Elsevier.

In the text
thumbnail Figure 24

Applications of salt hydrate PCMs in solar energy storage and utilization. (A) Solar water heating, adapted with permission from references [143145], Copyright © 2020, Elsevier, Copyright © 2018, Elsevier, Copyright © 2021, Elsevier, and (B) solar drying, adapted with permission from references [16,146,147], Copyright © 2014, Elsevier, Copyright © 2023, Elsevier, Copyright © 2021, Elsevier.

In the text
thumbnail Figure 25

Applications of salt hydrate PCMs in building envelopes. (A) A long-term real size experiment using salt hydrate PCMs [151,152], Copyright © 2020, Wiley, Copyright © 2018, Elsevier. (B) Numerical simulation of house integrated with salt hydrate PCMs [68], Copyright © 2020, Elsevier.

In the text
thumbnail Figure 26

Comparative study of organic PCMs and salt hydrate PCMs applied in building envelopes. (A) The life Cycle Assessment [153] (PCM1 and PCM2 denote organic PCMs and salt hydrate PCMs, respectively), Copyright © 2010, Elsevier. (B) The multi-objective ranking via Fuzzy AHP-Modified Fuzzy TOPSIS method [154] (S and SP both denote salt hydrate PCMs; A and RT both denote organic PCMs; PT denotes biobased PCMs), Copyright © 2021, Elsevier.

In the text

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