3.2.1. Year of Construction vs. Pre- and Post-Audit Water Use Intensity
Buildings in the UAE consume electricity either by direct consumption to operate AC units, with the costs added to the monthly electricity bill, or by being connected to a district cooling, in which case the AC bill comes separately from the district cooling company. These companies supply very cold chilled water to the occupants. The electricity bill of a home includes the electrical consumption of the unit, but the electricity consumption required to cool the water comes in the bill from the district cooling company that supplies the occupants with the chilled water. However, mosques have their own AC units within the building structure (not linked to district cooling), so the water consumption reported in the bill is the actual domestic water consumption. In contrast, in the buildings linked to district cooling, the chilled water consumption represents the chilled water consumed when the AC is turned on and not the water consumed when the tap is running water. Thus, the more the AC is kept on within the house, the more water from the chilled water network is consumed, which in turn increases the bill. Therefore, analyzing the rate of water consumption in mosques is beneficial for understanding their energy consumption patterns and to propose conservation measures.
Water use intensity (WUI) refers to the rate at which water is used in a given area. It is an indicator of how much water a building requires during its occupation. To determine the WUI, the year of construction (Y) of each mosque was analyzed against both the value of the pre-audit water use intensity (PWUI) and the value of the post-audit water use intensity (PAWUI) after implementing the water conservation measure in order to determine if the variable (Y) had an effect on the value of the WUI.
Among the 146 mosques studied, 136 mosques were analyzed for water consumption. Analyzing the association between the continuous variables (PWUI and PAWUI) and the categorical predictor of the year of construction (Y), it was clear that the older mosques had higher mean values of WUI than the newer mosques (
Table 7), which is observed in the difference between the PWUI before implementing the WCMs and in the PAWUI after implementing the WCMs, which indicates that older mosques had higher water consumption compared to newer mosques. This is expected due to the improvements and advancements in the strategies, technologies and systems employed in managing the water consumed in a given facility, from water system designs to leak detection and repair, which help make the consumption of water more efficient and lower the value of the WUI. It can also be seen that the mean values of the WUI among the three year categories decreased after implementing the WCMs, as follows:
1991–2000: from 2.21 to 1.26 (m3/m2);
2001–2010: from 1.79 to 1.24 (m3/m2);
2011–2017: from 1.42 to 0.95 (m3/m2).
The above analysis shows the success of implementing the WCMs in reducing the consumption of water.
3.2.2. Year of Construction vs. Water Savings
Upon analyzing the association between the continuous variable of the value of the total water consumption saving (TWCMS) in m
3/m
2 achieved after implementing the WCMs and the categorical predictor of the year of construction of the mosque (Y), it was clear that the mosques in the first category (1991–2000) had a higher mean value of TWSCMS than those in the second category (2001–2010) (
Table 8) and those in the third category (2011–2017). This indicates that the TWSCMS is reduced over the years after implementing the WCMs, as there is a lower margin of enhancements to make due to the advancements in the systems used in newer mosques. This is also evident from the year of construction vs. existing and post-audit water use intensity analysis, which found the following:
1991–2000: from 2.21 to 1.26 (m3/m2) with estimated savings for each mosque in this category of 0.95 m3/m2, disregarding the size variation of the mosques;
2001–2010: from 1.79 to 1.24 (m3/m2) with estimated savings for each mosque in this category of 0.55 m3/m2;
2011–2017: from 1.42 to 0.95 (m3/m2) with estimated savings for each mosque in this category of 0.47 m3/m2.
Overall, it can be concluded that the year of construction is a significant factor of the TWSCMS achieved and a significant contributor to the value of the WUI. Therefore, more focus should be directed toward older mosques because these existing old structures, which still have tens of years in their life spans, are inefficient when it comes to water consumption. By simply implementing WCMs, the water usage efficiency could be greatly improved.
3.2.6. Analysis of Water Conservation Measures (WCMs) Adopted and the Payback Period (PBP) for Each WCM
Upon performing the analysis and exploring the association between the continuous variable (PBP) and the categorical variable (WCM), it can be seen that A was the most cost-effective WCM, as it achieved the lowest mean value (0.4 year) of PBP, which means that in less than half a year, the cost of investment in this WCM would be covered and everything would be pure profit. This makes A the most attractive WCM to adopt, although it achieved less water consumption savings than the other the two WCMs (
Table 10), contributing to 30% of the water savings for all the mosques that were studied. It can also be seen that although WR achieved a higher mean value of WCMS% than A, contributing to 33% of the water savings of the total savings for all the mosques analyzed (
Table 10), it has the highest mean value (7.2 years) of PBP, which makes it the least attractive WCM to adopt, as evidenced by its implementation in only 14% of all the mosques that were studied.
Regarding water consumption in mosques, the previous reviewed research [
31] showed that the ablution process consumes a huge amount of water and requires access to more sinks compared to other buildings, such as residential or commercial buildings. Therefore, as shown in the current research, implementing self-closing faucets and using aerators can significantly reduce the water consumption and improve the sustainability of a mosque, as well as the potential for water recycling, especially in regions of water scarcity, such as the UAE.
Through the overall analysis, the older mosques showed higher energy and water consumption vs. the more recently built mosques. Accordingly, the potential energy savings of older mosques is higher than that of newly built mosques. In terms of the electricity consumption, it can be concluded with a 95% confidence interval that efficiently running mosques have a mean electrical consumption of 84 kW/m
2 per year. This can be used as an EPI to evaluate how efficiently a specific mosque is performing in comparison to the others. An average of 32% energy saving can be expected based on the average savings achieved within the collected data. Moreover, for water consumption, it can be concluded with a 95% confidence interval that efficiently running mosques have a water consumption mean of 1.18 m
3/m
2 per year. This can be used as a WUI index to evaluate how efficiently a specific mosque is performing in comparison to other mosques. An average of 38% water consumption savings can be expected based on the average savings achieved within the collected data. The detailed savings of the energy and water consumption measures (ECMs and ECMs) are presented in
Table 11.
Overall, for electricity consumption, an average saving of 17,860 kg of CO
2 per mosque per year can be achieved, and as the UAE has more than 9123 mosques, the potential environmental CO
2 savings could be 162,937 tons of CO
2 per year, which is more than the CO
2 emissions of Samoa, Comoros or the British islands [
32]. In addition, considering the average area of the studied mosques, the total financial savings per mosque would be 40 kW/m
2 × 2377 m
2 × 0.45 = 42,786 AED/year, and when applied to all of the mosques within the UAE, as per the data from the year 2020, the total financial savings across the UAE is estimated to be 42,786 × 9123 = 390,336,678 AED.
For water consumption, an average saving of 726.80 m
3 per mosque per year can be achieved, and as the UAE has more than 9123 mosques, the potential water savings could be 6.62 million m
3 per year. The total water consumption of the Maldives and Monaco is less than 4.54 million m
3 per year [
33]. Considering the average area of the studied mosques, the total AED savings per mosque is expected to be 0.7267990625 m
3/m
2 × 2479 m
2 × 13.208602618 AED/m
3 = 23,798.4 AED per year, and when applied to all of the mosques within the UAE, as per the data from 2020, the total savings in Dirhams across the UAE is expected to be 23,798.4 × 9123 = 217,112,803 AED per year.
The behavioral aspects of mosque occupants should also be considered and assessed if the target is to induce a behavioral change within the society that is home to mosque occupants or visitors. Increased activity in a mosque is correlated with the lunar calendar and Islamic events, as well as the five-times daily prayers of 0–60 min each (with Fridays having a special two-hour, more crowded occupancy for AlDuhr Prayers), which could be properly managed by implementing measures such as water recycling or HVAC system customization [
34]. It is also recommended to further investigate the source of energy consumption or water usage, such as electrical utilities (sound systems, fans and water heating machines), or the exact locations within the mosque that are more demanding of energy and water, such as the Imam headquarters, ablution or toilet spaces, gardens or Mouazzin Minbar, which could provide a better understanding of the actual consumption patterns and how to improve the related processes.
Overall, the design of mosques should be properly assessed and studied at an early stage to address the various forms and elements of mosques, such as mihrab, patios, minbar and corridors, as well as ablution areas, toilets and the external surroundings, such as the garden, all of which dictate the electricity and water demands. Historically, mosques have had varying designs [
35], such as Moorish, Andalusian, Egyptian, Seljuk, Indian, Safavid and Ottoman, and different shapes, such as Arab, Persian and Ottoman. In the Gulf Region, it is also critical to consider the geographical climate or the cultural conditions that affect the design of mosques, all while keeping in mind the energy and water demands that result from their design. Similar studies addressing commercial and residential buildings that have undergone energy audits should be conducted to provide a comprehensive overview of energy and water consumption and the effect of implementing ECMS and WCMs within the context of the UAE.