Discussion
Economic analyses related to housing and health have been summarised in the WHO guideline5 and systematic reviews.20 In New Zealand, cost-benefit analyses were performed to evaluate the effect of retrofitting houses with insulation based on a randomised community-level trial,21–23 and an insulation subsidy programme.24 They revealed that the savings achieved by improving health conditions dominated the costs of insulation retrofitting. An earlier analysis on retrofitting insulation in the USA also showed that the benefits including energy savings and productivity benefits outweighed costs.25 However, these studies do not include the benefits gained from preventing CVDs, which are the leading cause of death globally and are caused by cold temperatures inside the house. Among previous studies addressing CVDs, one published paper26 estimated the impact of eradicating cold housing on health in Australia, finding that it was comparable to the effects of lifestyle and dietary interventions. However, this study did not provide a detailed quantification of the associated costs. In the UK, a report by the Building Research Establishment estimated the cost-benefit of improving poor housing based on the Housing Health and Safety Rating System, indicating that the savings generated by mitigating hazards in poor housing were £18.5 billion (US$22.4 billion) per year and that improving excess cold contributed to a large amount of the savings.27 Another study showed that upgrading windows and doors to double-glazed ones and installing wall insulation decreased emergency hospital admissions and generated considerable estimated savings using longitudinal data.28 However, these two studies showed the evaluation of QALYs as one of their future challenges. Among previous studies that evaluated both the costs and effectiveness (measured in QALYs) related to CVDs, one study29 based on mathematical modelling demonstrated the effects of energy efficiency interventions in the UK. According to this study’s findings, the impact of investments in home energy efficiency mostly exceeded the ICER threshold in the UK. This may be attributed to the relatively higher indoor temperatures before the interventions in the UK compared with the lower indoor temperatures in Japan, resulting in a diminished effect of temperature increases due to energy efficiency interventions.
In this context, it is necessary to consider whether low indoor temperatures are a problem unique to Japan. According to prior research, cold homes represent a challenge not only in Japan but also in other countries. In a study conducted in Asia, the average morning temperature in 114 Chinese households during winter was 15.3°C.30 Another study conducted in China revealed indoor temperatures ranging from 0.5°C to 24°C during the winter months in 527 residential buildings.31 In India, an investigation of 150 vernacular homes across different seasons indicated that mean indoor temperatures were lowest in January, dropping to 13.7°C in Imphal, 15.0°C in Cherrapunjee and 17.2°C in Tezpur.32 In Oceania, environmental measurements revealed a winter average temperature of 16.5°C in 100 Australian houses.33 A New Zealand study that monitored indoor temperatures in 397 houses during winter found that the average living-room temperatures during the day and bedroom temperatures at night were 15.8°C and 13.6°C, respectively.34 In Africa, year-long measurements of 100 houses across five towns in Tunisia revealed minimum indoor temperatures ranging from 4.8°C to 15.7°C.35 In Europe, the average indoor temperature during winter in 141 Portuguese households was 14.9°C in bedrooms and 16.6°C in living rooms.36 A study of 43 Greek houses reported an average temperature of 15.9°C.37 Conversely, a review of measured indoor temperature in UK homes indicated that the average living room temperature in winter ranged between 18°C and 21°C.38 The Energy Follow-Up Survey 2017, which involved 750 UK dwellings, revealed an average indoor temperature of 18.4°C during the heating season (December to February).39 In France, the average temperature in 384 houses was reported to be 20.0°C.40 In the USA, the average temperature across 327 homes in various climate zones during the heating season was 19.6°C.41 Despite these relatively high averages of indoor temperature, energy poverty remains a prevalent problem even in both Europe and the USA,42 43 leading to the widespread issue of cold homes. Furthermore, the recent surge in energy prices has exacerbated the problem of energy poverty, increasing the global challenge of living in cold homes.44
In summary, the results from most previous health economic analyses and the present analysis are generally consistent in showing that thermal insulation work on houses could be beneficial. However, the studies vary widely: some consider only costs, others focus solely on health impacts, and some account for both. Additionally, the health indicators and productivity losses included differ across studies. This variability in prior research, where health improvements can lead to savings that exceed the costs for thermal insulation work on houses, contrasts with our study, which found that these costs were not fully recouped. Furthermore, most previous studies focus on specific insulation programmes in particular areas or countries, which weakens the generalisability of the findings. According to the systematic review,20 a key limitation of previous analyses is that evidence from one setting is difficult to transfer to another. In contrast, a major strength of the present analysis is that the model is established based on the association between BP and indoor temperature, which are internationally generalisable indices. Through the aforementioned review on indoor temperature, it is evident that the problem of cold homes is prevalent worldwide, thus generalisability is an important aspect. In addition, the causal relationship between hypertension and CVDs is well established based on abundant previous research. Therefore, the framework of the economic model suggested in this paper is expected to be applicable to other situations by adjusting the model inputs.
The present study has several limitations. First, the suggested model only included the health status of hypertension and CVDs. For example, the prevention effect on respiratory diseases, which are also affected by low indoor temperatures, was not included.5 45–47 This was because quantitative evidence on the association between indoor temperature and generalisable respiratory indices (eg, forced expiratory volume in 1 s and forced vital capacity) is limited at present. A systematic review48 and a recent study49 also showed that residents’ mental health declines when their houses have disadvantages, or when they can no longer afford to warm their homes. Thus, the inclusion of health statuses not related to hypertension and CVDs is expected to contribute to multiple benefits that support the importance of housing. On the other hand, considering health statuses beyond hypertension and CVDs might lead to increased medical costs for other diseases, such as cancer (the second highest medical expenditure following CVDs in Japan) due to the prevention of CVDs and longer lifespans in upgrading and retrofitting insulation scenarios. Future research should aim to develop a comprehensive model that can evaluate other health statuses and their associated costs once further quantitative evidence becomes available. Second, only a husband–wife pair was included, and other family members (eg, children) were not considered. Given that respiratory diseases are more prevalent in children, this might be one of the causes of underestimation. Third, previous research50 has shown that reducing ventilation to maintain indoor temperatures during winter can lead to increased indoor radon concentrations, thereby increasing the risk of lung cancer. Therefore, it is necessary to comprehensively assess the living environment, including ventilation.51 52 In this context, it is also essential to consider PM2.5 (particulate matter less than 2.5 micrometers in diameter) as it moves from outdoors to indoors through ventilation, and has a significant impact on health.53 From the perspective of indoor air quality, the type of heating used warrants further examination. Although the present study focused on non-polluting types of heating devices, there are still heating devices that pollute indoor air in real life settings. In fact, a randomised controlled trial in New Zealand, which involved the installation of non-polluting heaters, showed significant benefits in preventing respiratory diseases.54 55 Finally, 40-year-old/60-year-old husband–wife pairs in Japan were evaluated as a first step. Therefore, the results may vary when considering populations in other countries. However, the present economic model can consider various conditions flexibly by changing the inputs to the model. For example, although the temperature–BP relationship obtained from the Japanese population was used in this study, it should be adjusted to reflect the relationships in other populations.56 Of note, although the present study considered the difference between men and women in the indoor temperature–BP relationship, recent papers and guidelines have criticised the treatment of gender as a binary factor (male/female).57 58 Simplification is a necessary process in creating a health economic model, but the limitation of considering only husband (male)–wife (female) combinations should be noted.
In conclusion, the present study suggested a mathematical economic model to calculate the cost-effectiveness of living in well-insulated warm houses using general indices based on the combination of the indoor temperature–BP relationship and BP–CVD relationship obtained in previous studies. Using this framework, it was indicated that (1) 74.1% and 57.9% of the expenses incurred from upgrading the thermal insulation level from Grade 2 to Grade 4 and Grade 6, respectively, were recouped, mainly due to the reduction in medical costs from living in warmer houses; (2) In a similar manner, 35.4% and 42.6% of the expenses associated with retrofitting thermal insulation from Grade 2 to Grade 4 and Grade 6, respectively, were recouped; (3) When taking the healthy life expectancy of a husband–wife pair into consideration, upgrading the thermal insulation level when purchasing new houses could be cost-effective strategies, with ICERs below the threshold value of JPY5 million/QALY gained; and (4) The probabilistic sensitivity analyses showed that retrofitting insulation in entire existing houses from Grade 2 to Grade 6 and maintaining a temperature of 21°C emerged as the most cost-effective options when WTP reached JPY6.5 million or more, indicating the necessity of considering lower-cost methods such as partial insulation retrofitting.
The authors believe that this feasible modelling study will aid in systematic decision-making on housing and health for several stakeholders. The authors also anticipate that these interdisciplinary findings will facilitate the widespread adoption of well-insulated houses, contributing to sustainable development in terms of not only Sustainable Development Goal (SDG) 3 (health) and SDG 11 (sustainable cities) but also SDG 10 (reduced inequalities) and SDG 13 (climate change).