Introduction

The world energy consumption and associated CO2 emission are increasing at an unprecedented rate due to population growth and globalization effects. The contribution from the building's structure to global energy consumption has gradually increased which accounts for almost 1/3rd of the greenhouse gas emissions [1]. This is because buildings represent a significant percentage of the world’s energy consumption and associated CO2 emissions [2]. For instance, in the US. and Europe, the energy consumption due to the building sector represents 39–40% while 36–38% is due to CO2 emissions [3]. In the case of the Kingdom of Saudi Arabia (KSA), the energy consumption due to the buildings is about 70% of the total electrical energy consumption of the country [4,5,6]. Due to urbanization and population rise, the demand in infrastructure is rising, which leads to the higher consumption of building material, particularly ordinary Portland cement (OPC) [7]. The major drawback of manufacturing ordinary Portland cement is its energy-intensive process which contributes to high emissions of CO2 into the atmosphere. Previous studies indicate that 2% of the world’s energy and 5% of the world’s industrial energy are consumed by the cement industry sector, which accounts for emitting 5% of CO2 emissions and it is one of the largest sources of anthropogenic emissions of CO2 [8]. This prompted the development of green construction products using alternative materials. Numerous studies have explored the possibility of utilizing solid wastes and found them superior for construction [9,10,11,12]. Such agro-industrial wastes-based researches incorporated wood waste ash [13], natural pozzolan [14], fly ash [15], rice husk ash [16], date palm ash (DPA) [17], palm oil fuel ash [11], metakaolin [18], silica fume [19], ground granulated blast furnace slag [20], and superpozz [21] exhibited excellent performances.

In the recent past, there has been growing interest in the utilization of by-products that are disposed of as solid stockpiles and landfills, to recycle them as supplementary cementitious materials (SCMs) due to their economic, environmental and technical merits. Several studies reported the potential and optimum dosage of SCMs to be partially mixed with OPC, and its effects on mix design, exposure conditions, and performance with concrete [15, 17, 22,23,24].

Khalil and Algamal [7] examined the Partial Replacement of Ordinary Portland Cement with local natural Minerals from Jeddah regions of KSA. The authors found the specimens’ mechanical and economical aspects were improved significantly. Zeyad et al. [25] investigated concrete mixtures prepared with two sets of volcanic pumice powder (VPP) and polypropylene fiber. They conducted the lab test and found tensile and flexural strengths were optimized at 10% VPP. Kannan et al. [26] examined the High-performance concrete (HPC) mixtures incorporating 10–40% Ceramic waste powder (CWP) as replacement of Portland cement, and found that the specimen exhibits high strength and excellent durability while microstructure investigations showed that there was no significant difference in cement hydration compared to the cement without CWP. Singh et al. [27] investigated the effect of partial replacement of cement by waste marble slurry in Rajasthan, India. The authors performed the laboratory test and found the mechanical properties of concrete enhanced with the incorporation of dried marble slurry up to 15% replacement. Ismail et al. [11] performed the laboratory test on the bricks fabricated from paper sludge and palm oil fuel ash (POFA). They found that the brick made with 60% cement, 20% sludge and 20% POFA satisfies the standard for precast concrete masonry units.

Kupwade-Patil et al. [28] studied the effect on Embodied Energy Coefficients (EEC) when Ordinary Portland Cement (OPC) was partially substituted by natural Pozzolanic Volcanic Ash (VA). They found that the replacement of OPC with volcanic ash decreases by about 16% in EEC. Blaisi [29] experimentally conducted the environmental assessment of utilizing date palm ash as partial replacement of cement in mortar and found that the DPA poses no environmental risk to human health when used as a cement replacement. A study [30] of the utilization of date palm fibers (DPF) with cement and sand has found that 5%, 10%, and 15% of DPF loading in the mortar yield good thermal and mechanical properties of the composite which could be used as the energy efficient building components.

The literature review reveals that a substantial amount of research has been carried out, and researchers are still underway, to exploit the benefit of replacing the OPC with solid waste in improvising the thermal, environmental, physical, microstructural aspects of the composites. Recently, Al-Kutti and co-workers [17, 22, 23] experimentally evaluated the mortar specimen prepared by the partial replacement of OPC with DPA in the proportion of 10–30% and found that mechanical, durability and microstructural performance of the specimens were enhanced. Moreover, mechanical and durability property values satisfy the relevant international standards with the DPA dosage up to 30%, whereas the optimum value was obtained for the mortar specimen with 10% DPA. However, the thermal and energy performance of the novel DPA blocks have not been explored. Accordingly, the current focus of the study is to examine the impact of DPA loading on thermal characteristics, energy consumption, and indoor environment of the building. The findings promote application of DPA in block making to valorize generation of date palm waste, minimize the cost of construction as well as operational cost of the building, and maximize the sustainable practice in the construction industry.

Materials and methods

Materials

Ordinary Portland cement (OPC)—Type I in compliance with ASTM C150 was used in each mixture. DPA was procured from the date farm at Al-Hasa city located in the Eastern region of Saudi Arabia. DPA was produced as an aftermath of burning waste date tree fronds that is continuously supplied as a fuel material during the production of charcoal from the firewood. The stages of DPA generation are depicted in the form of a flow chart in Fig. 1 [31].

Fig. 1
figure 1

DPA generation process

Specimen preparation

The mortar cubical specimens of 50 × 50 × 50 mm size were prepared using 100% OPC (control mix) and the partial replacement of OPC by DPA with the varying dosage as summarized in Table 1. The samples were designated as OPCx-DPAy where x and y represent the percentage of OPC and DPA, respectively. For example, OPC90-DPA10 means cementitious material consists of 90% OPC while DPA is 10%. The density of the cementitious material was 350 kg/m3, water to the cementitious material ratio (w/cm) was maintained 0.4 while cementitious material to sand ratio was kept 1:2.10 in all mixtures.

Table 1 Mixture proportion

Experimental investigation of thermal characteristics and density

The equivalent thermal conductivity (k) and specific heat capacity (Cp) test of the control and DPA-based mortar were performed by the transient hot bridge (THB) method with the analyzer Linseis THB-100, Germany.

The Transient Hot Bridge is based on a non-steady state or time depended measuring method. The advantage of this method compared to the steady-state model is shorter measuring time, and it can measure thermal diffusivity in parallel to the thermal conductivity. The measurements comply with ASTM D7984 and ISO 22007-2 standards. The electrical current of 75 mA was applied to the strip-shaped sensor, model THB6K77, which was used as heater and temperature sensor, embedded between the identical samples of thickness 50 mm, measurement time ranged between 60–100 s [33]. The pictorial and schematic view of the test set-up is illustrated in Fig. 2a and b. The strip emits a constant heat flow during the measurement, causes a rise in temperature. The temperature rise over time corresponds to the thermal transport properties of the sample. The properties such as thermal conductivity, thermal diffusivity, and the specific heat capacity were evaluated by solving complex thermal conductivity equations through a known power input and temperate raise [34]. It was ensured that the Linseis THB-100 was calibrated before each measurement with materials of known thermal conductivity polymethyl methacrylate (PMMA). Multiple measurements were performed for each sample and their average values were recorded.

Fig. 2
figure 2

Test set-up for thermal conductivity test. a Pictorial view, b schematic view

Building description and Simulation

To assess the thermal effectiveness of mortar blocks comprising OPC and DPA, energy simulations were performed on a typical office building located at Dhahran, KSA. The specification of the studied building is summarized in Table 2. The data such as Lighting power density (LPD), Equipment power density (EPD), Occupancy, and set point temperature complied with ASHRAE standard [35, 36]. The thermal characteristics and density value obtained experimentally (Table 3) were used in the simulation program to estimate the energy performance of masonry block specimens (Table1), used as a structural component in the external wall. Figure 3 illustrates the external wall structure used in the current study which is the local practice and in compliance with the Saudi Arabian standard [37, 38]. The studied building was modeled and simulated in DesignBuilder (Version 6.1.06). DesignBuilder is the interface of Energy Plus simulation engine, uses dynamic parameters to produce detail environmental performance data. The calculations are based on heat balance technique considering the simultaneous interaction of building models with outdoor weather conditions to evaluate the various loads on an hourly basis. The physical characteristics of the building model are summarized in Table 2. Figure 4 illustrates the climatic profile of Dhahran. It is evident from the figure that hot climate prevails over almost 10 months of the year, representing a typical cooling-dominated climate. Figure 5 illustrates the annual sun path with hourly solar angles over the base-case building model. The rationale of modeling Dhahran city is justified because its climate is categorized as an extremely hot and humid climate [39].

Table 2 Building specification for simulation program
Table 3 Thermal conductivity, specific heat capacity and density of masonary block sample
Fig. 3
figure 3

Schematic of wall configuration

Fig. 4
figure 4

Climate profile of Dhahran, Saudi Arabia [Courtesy: climatemps.com]

Fig. 5
figure 5

Annual sun path over Building model

Validation and calibration of simulation program

The validation and calibration of simulation results were done by monthly electricity consumption billing records of an existing office building in Dhahran, KSA. The building was modeled in the simulation program and all the parameter such as occupancy, lighting power density (LPD), equipment power density (EPD), HVAC system, were inputted, which are recorded from the existing office building and are also in compliance with ASHRAE standard [36]. Figure 6 shows the monthly electrical energy consumption for the building base-case model predicted by the DesignBuilder and the actual energy billing for the year 2017. It is worth noting that there is less than 2% difference in result between the simulation program and the utility bill data which is lower than that reported by Iqbal and Al-Hamoud [4], who studied the energy conversion measures for an office building, in the same region of KSA, and therefore could be considered reasonably acceptable.

Fig. 6
figure 6

Comparison of monthly energy consumption predicted from simulation program and actual electrical consumption (2017)

Results and discussion

Thermal conductivity results of the specimens were first presented to understand the effect of DPA dosage on thermal characteristics followed by estimating the annual energy consumption. Then effect of DPA on unit cost of the specimens was reported.

Thermal characteristic and density

The thermal conductivity, specific heat capacity, and density values were evaluated experimentally for various developed blocks are summarized in Table 3. For determining the thermal characteristic, transient hot bridge method was used. Obtained thermal conductivity of the developed blocks and the control block is given in Table 3, the control specimen properties are similar to the commercially available masonry block. The observed thermal conductivity values vary in between a minimum of 0.432 W/mK for the specimen with 30% DPA (Type 4), and a maximum of 0.81 W/mK for the control specimen (Type 1). This result is in close agreement with that of Al-Dharmi and Iqbal [40] who studied the thermal performance of different types of masonry blocks used in Saudi Arabia and found that the thermal conductivity of the masonry block was 0.83 W/mK. The thermal performance of block follows a similar pattern as that of density which points out to the fact that the proportion DPA content is significant in lowering heat transfer rate through the material. The porosity of the DPA-based block is higher than the control block, as reported in the author’s previous study [24], thus affecting the overall thermal conductivity of the material. The thermal conductivities of specimens with 10% DPA (Type 2) and 20% DPA (Type 3) are 0.693 W/mK and 0.573 W/mK, respectively. It is worth noting that the reduction in thermal conductivity of the specimen with 30% DPA (Type 4) compared to the control specimen (Type 1) is 46.67%. These findings are in good agreement with the previous study [41] on thermal conductivity of mortars containing polyurethane waste particles, which reported a maximum of 20% decrement in thermal conductivity could be achieved by the mortar mixture containing 30% polyurethane. The decrement in thermal conductivity has also been reported by Milani and Labaki [42], who analyzed the masonry block prepared by the partial replacement of cement with rice husk ash and compared with the normal masonry block.

The thermal resistance (R-value) of the commercially available mortar block (Type 1) and the blocks prepared with DPA are compared in Fig. 7, while the percentage increase in thermal resistance by the addition of DPA is shown in Fig. 8. It can be observed that Type 4 specimen has 47.4% higher thermal resistance compared to control specimen (Type 1), followed by Type 3 (28%) and Type 2 (9.6%) in decreasing order of efficiency. This trend correlates with thermal conductivity data of the present study and also reported elsewhere [40, 43,44,45,46,47,48,49,50,51,52,53]. It is worth mentioning that the density of the blocks decreases with increase in the DPA content such that the reduction of 3.57%, 5.24% and 7.14% corresponding to type 2, 3 and 4 block are respectively recorded (Table 3), owing to the less bulk density of DPA particles. The density values fall in the range of 650–1500 kg/m3, which follows the ASTM C55-11 standard [54] for light weight masonry block. Thus, the decrease in density of the block with the addition of DPA is advantageous in producing lighter masonry blocks which consequently contribute to the reduction in self-weight of the building structure.

Fig. 7
figure 7

Comparison of thermal conductivity among different types of blocks

Fig. 8
figure 8

Thermal resistance and Percentage variation among different types of blocks

Monthly cooling/heating loads and total energy consumption

Annual Energy consumption

The density and thermal characteristics of the block specimens estimated through experimentation were used as the input data in the simulation. To explore the energy performance, masonry blocks are used as a structural component of the wall profile as summarized in Table 4, the wall configuration is commonly used in KSA [38].

Table 4 Structure of investigated wall

To assess the impact of DPA block on the energy performance of the building, the annual energy and cooling energy consumption by various wall options were estimated, as plotted in Fig. 9. With respect to the control specimen (Wall 1), the energy-saving potential of the various wall options were also determined (as a percentage of base case) as shown in Fig. 10. It is evident that wall 2 and 3 produced the saving of 6.3% and 7% respectively, although the DPA content in the block was increased from 10 to 20%. This is due to the fact that heat gain through the wall is lower compare to the other building structural components [55]. It is observed from Fig. 11 that the Energy Use Index (EUI) and cooling load intensity are reduced to 238.6 kWh/m2/year and 155.3 kWh/m2/year respectively, by replacing wall 1 (0% DPA) with Wall 4 (30% DPA). This is attributed to the fact that density, specific heat, and thermal conductivity of the structural elements play a crucial role in the heat gain of the building [4, 56,57,58]. Moreover, increment in the thermal resistance reduces the cooling load and vice versa.

Fig. 9
figure 9

Annual energy consumption and cooling load for various wall options

Fig. 10
figure 10

Energy-saving potential of various wall options compare to base case (control specimen)

Fig. 11
figure 11

Cooling Load Intensity and Energy Use Index for various wall options

It has been found that the cooling load is 65% of the total energy consumption of the building, which is mainly the combination of internal loads (lighting, occupancy, equipment) and heat transfer through the building fabric. This observation is consistent with research conducted by Al-Ugla et al. [59]. The energy-saving potential of Wall 2 is observed to be 9.4%, which has been increased to 10.5% (Wall 3) and 11.3% (Wall 4), with an addition of 10% and 20% of DPA content respectively.

Indoor air temperature

Impact of wall type on the indoor air temperature of the building was estimated, as plotted in Fig. 12. The data in the figure indicates the maximum indoor temperature is in the month of August, as the outdoor dry bulb temperature is highest during that period (Fig. 4). The results are consistent with those observed in the monthly variation of the cooling load in Fig. 13. In general, it can be observed that the cooling load starts escalating from March, reaches to peak in August, declines and reaches a minimum during January. This is consistent with the average monthly solar incident radiation of the study location as shown in Fig. 4. The average simulated value of the highest indoor air temperature for the building, with wall 1 (control specimen) was 26 °C, whereas the maximum temperature for the building with wall 4 (30% DPA) was 24.2 °C. An important issue emerging from this finding is that the average indoor temperature is reduced by 2 °C. This can be attributed to lower U-value of DPA-based block compare to the conventional masonry block which acts as a good thermal insulator. It has been well established that wall insulation plays a crucial role in improving energy consumption and indoor thermal environment [60].

Fig. 12
figure 12

Average monthly indoor temperature variation for various wall options

Fig. 13
figure 13

Monthly variation in cooling Energy consumption

Cost of masonry block

The unit cost of the novel masonry blocks were evaluated, it depends on the raw material cost. The costs of the raw material, used for comparison purposes are shown in Table 5. It can be observed that the important component affecting the cost of the masonry blocks is the cement (Table 5). As compared to the conventional masonry block, DPA-based masonry blocks were found to be economical as DPA is the waste material. The unit cost of the bricks for all the options is tabulated in Table 6. It is apparent from Table 6 that the unit cost of the control block (Type 1) is highest, due to the high content of OPC while the unit cost of the DPA-based masonry (Types 2, 3 and 4) blocks decreases with the increase in the proportion of DPA.

Table 5 Raw material cost
Table 6 Unit cost of masonry block

The percentage decrease in the unit cost of DPA-based blocks with respect to conventional masonry block (Type 1) was also determined as shown in Fig. 14. The decrement in the unit cost of Type 2 block is observed to be 15.15%, which has been further decreased to 35.71% (Type 3) and 58.33% (Type 4), with the addition of 10% and 20% of DPA content respectively. Therefore, it can be posited that the reduction in manufacturing cost of masonry blocks is effected by percentage replacement of OPC by DPA.

Fig. 14
figure 14

Percent decrement in unit cost of DPA-based blocks compared to control block (Type 1)

Conclusion

The thermal and energy performance of the novel masonry blocks prepared by the partial replacement of ordinary Portland cement (OPC) with date palm ash (DPA) in the varying dosage of 10, 20 and 30% were explored. Simulations were carried out employing DesignBuilder software on a typical existing office building located in the Eastern region of Saudi Arabia (Dhahran). The findings of the research are quire convincing, and thus the following conclusions could be deduced:

  • The developed masonry blocks fall under the light weight block category in accordance with ASTM C55-11 standard, based on the density of masonry blocks prepared with 10–30% DPA replacement.

  • The increase in thermal resistance (R-value) of the block loaded with 10%, 20%, and 30% DPA in comparison to control block (0% DPA) were 9.6%, 8.1% and 47.4% respectively.

  • The annual energy consumption and cooling load of the building having type 3 block (30% DPA), can be reduced by 7.66% and 11% respectively, compared to the control block (0% DPA).

  • DPA content in the masonry block (Type 4) is a promising option for reducing heat stress inside the building. It could reduce the average monthly indoor temperature by 2 °C.

  • A cost-saving of 11.3% in the annual energy consumption of the building could be yield with the usage of DPA-based blocks as compared to the conventional masonry blocks.

  • The cost analysis shows that DPA-based blocks with 30% DPA (Type 3) is most effective among the studied blocks as it has the unit cost of 2.76 $/m2.

Further studies, which take Life cycle assessment (LCA) and Life cycle cost (LCC) of DPA block options are underway which will be published in due course.