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Scientific Data volume 9, Article number: 285 (2022 ) Cite this article
Rising temperatures are causing distress across the world, and for those most vulnerable, it is a silent killer. Information about indoor air temperature in residential dwellings is of interest for a range of reasons, such as health, thermal comfort and coping practices. However, there have been only few studies that measure indoor heat exposure, and contrast these to outdoor temperatures in rural-urban areas, of which none are in South Asia. We aim to close this knowledge gap with our indoor and outdoor heat measurement dataset, covering five low-income sites in South Asia. Two sites are in rural areas (Maharashtra, India), while three sites focus on urban areas (Dhaka, Delhi and Faisalabad). Data are based on 206 indoor temperature data loggers and complemented by data from five outdoor automated weather stations. The data-set can be used to examine temperature and humidity variation in low-socioeconomic status households in rural and urban areas and to better understand factors aggravating heat stress. This is important to plan and implement actions for combating heat stress.
Global warming is increasing the incidence, intensity, and duration of heat waves1,2,3,4. In the last decade, heat waves have caused more mortalities globally compared to any other climate-related disasters5. The deadly heatwave of 2015 in India and Pakistan, which lead to more than 3600 deaths6, has only confirmed the health threats emerging from heatwaves even for those accustomed to high temperatures.
The negative health impacts of longer and more frequent and intense heat waves will disproportionately affect the warmer and poorer regions of the world7. With one-fifth of the world population, South Asia could be one of the first densely populated places in the world to experience deadly heat waves with meteorological conditions exceeding survivability thresholds8,9. India, Bangladesh and Pakistan are projected to be severely affected by changes in weather patterns. Besides the direct impact on health, this could lead to an overall decrease in per capita consumption expenditure and gross domestic product10.
Weather parameters that define human thermal comfort and exposure to heat stress are air temperature, airflow (wind speed), humidity and radiation. Outdoor environmental factors that affect heat stress are degraded landscapes, low vegetation cover, and high settlement density11. In the indoor environment, factors influencing heat stress, in addition to outdoor weather parameters, are the building style, characterised by material type and construction of the roofs and walls, ventilation, internal and external shading, and the application of cooling devices (air conditioner, evaporative cooler or fan). The quantity of heat transmitted by, for example, different roof types determines the amount that is radiated inside and thus influences indoor temperature12.
Heat stress has various impacts on human health. Increased heat stress is generally associated with significant excess all-cause mortality13,14. Increased morbidity and occupational vulnerabilities are much more common. High temperatures are linked to multiple clinical syndromes such as heat stroke, heat exhaustion, heat syncope, and heat cramps15. Workers exposed to outdoor heat stress have reduced work productivity, experience physiological distress and adverse health impacts16,17,18. At night, high temperatures affect the quality of sleep, with prolonged exposure suggested to have significant impact on cognitive capacaties and people’s health. An increase in long term human migration has also been reported as a result of heat stress19.
Neighbourhood characteristics and properties of residential structures have a strong impact on heat exposure, heat stress and mortality. The poor and those from low socioeconomic status are more vulnerable to heat stress20,21. A study in South Africa found that living in wealthy areas and corresponding housing types may reduce heat related mortality by 50%22. In densely-built informal neighbourhoods in South Asia, exposure tends to be enhanced during night-time compared to exposure in green and open wealthier neighbourhoods21. Chronic heat stress, characterized by prolonged exposure also at night, as experienced by residents of informal settlements, is likely underestimated by studies using only outdoor weather station data23.
It is crucial to measure actual heat exposure of people in different indoor and outdoor settings to assess the relation between heat exposure and human health. Most epidemiological studies rely on meteorological data from standardised outdoor weather stations which may not accurately reflect personal heat exposure, such as inside houses or in areas with a landscape with very different characteristics24. A better understanding of indoor thermal conditions is essential because people spend most of their time in the indoor environment.
To fill this gap, a dataset of indoor temperature and relative humidity for low-income housing in five rural and urban sites has been created. Indoor temperature measurements were carried out in villages in Yavatmal and Jalna (Maharashtra, India), and the cities of Delhi (India), Dhaka (Bangladesh) and Faisalabad (Pakistan). These were supplemented by outdoor temperature and humidity measurements to gain better insight in temporal and spatial differences between indoor and outdoor temperature and humidity and the heat stress indicators that can be derived from these variables.
These measurements may help to understand indoor temperature variations in different housing types across various geographic locations in South Asia. Researchers, non-government organisations (NGOs)/civil societies working on public health issues, government departments (health, housing and disaster management authorities) and those engaged in policy formulations might find this dataset useful to plan and design actions for combating heat stress in indoor and outdoor environments. This dataset can be used to analyse the variations of temperature in different housing types and compare it with outdoor temperature. Those involved in the design and execution of Heat Action Plans and related heat warning systems can use the data to tailor warnings to expected indoor conditions in low-income settings which often differ from those observed outdoors.
Our indoor heat assessment is based on ambient temperature and relative humidity data. To complement the indoor data and provide direct comparison with outdoor temperature we have included outdoor observations from Automated Weather Stations (AWS) installed in the vicinity of the indoor study sites. An AWS is an automated version of the traditional weather station, and will typically consist of a weather-proof enclosure containing the data logger, rechargeable battery, optional telemetry to transfer data and the meteorological sensors with an attached solar panel or wind turbine and mounted upon a mast. These AWS measured air temperature (0Celsius), relative humidity (%), wind speed (km), and solar radiation. The period for urban indoor and outdoor measurements varied between the different study sites, but measurements were conducted mainly during the summer seasons of 2016 to 2018. Table 1 provides the details for each study site, data logger numbers and duration of data collection.
Indoor and outdoor observations were carried out in Delhi (India), and two villages in the Yavatmal and Jalna districts of Maharashtra (India), Dhaka (Bangladesh) and Faisalabad (Pakistan) (refer Fig. 1). Yavatmal and Jalna represent rural study sites while Delhi, Dhaka and Faisalabad are fast growing cities where temperatures are affected by the build-up surroundings, a process known as the urban heat island (UHI) effect. UHI is a phenomenon where urban areas are warmer than rural areas on average and this is often particularly pronounced during the evening and night25.
Case study sites, rural (blue) and urban (purple).
Most parts of South Asia suffer from spells of hot weather termed as heatwaves from March to June. April and May are known as the hottest month in the region. Yavatmal district is part of the Vidarbha region of Maharashtra, located in the central part of India. Many cities from this region feature among the hottest cities in the world. Jalna district is located in the central part of Maharashtra state in the northern Marathwada region. Recurrent droughts and parched landscapes characterise this region. The climate in both regions is classified as semi-arid, with hot and dry summers with relative humidity between 20% and 25% in the afternoon and moderately cold winters. The temperature starts rising from March till May, which is generally the hottest month of the year with a mean daily maximum temperature of about 42 °C in the Vidarbha region26 and up to 43 °C in the Marathwada27.
Delhi is the national capital of India and its second-most populous city, with about 29 million inhabitants. Of the nearly 1500 km2 total area, urban build-up areas cover about 700 km2 28. The weather swings from hot and humid in summer to cold and dry in winter. During the summer months, the capital region’s daily maximum temperatures can rise to 40–45 °C, while in winters, daily minimum temperatures can drop to 2–3 °C29.
Faisalabad is the third-most-populous city in Pakistan with an area of 1300 km2 and a population of 3.4 million. The district is located in the semi-arid region, characterised by erratic rainfall30. The city experiences temperatures on both end of the spectrum, with summer temperature extremes as high as 50 °C and winter temperatures as low as −2 °C. The mean minimum and maximum temperatures in summer are about 27 °C and 39 °C31.
Dhaka, the capital of Bangladesh, covers an area of about 306 km2 and has a population of about 21 million inhabitants. The climate of Dhaka can be classified as a tropical savanna climate, with a distinct monsoonal season. The highest daily maximum temperatures are reached in March-May, rising to nearly 40 °C on individual days with the average being about 33 °C. Furthermore, a high average minimum temperature of over 26 °C is observed in the monsoon months June- August. These months are extremely humid, with an average evening relative humidity of about 75% and an average morning relative humidity of about 93%21.
The target populations in both the rural and urban areas were low-income households, a large socio-economic class in all three countries. India has the largest number of people (364 million people, 28% of the population) classified as multidimensional poor, as per the 2018 global Multidimensional Poverty Index (MPI)23. This index considers 11 indicators, spread across three dimensions of poverty- living standards, education and health. Pakistan and Bangladesh have similar percentages of poor people, and are ranked 4th and 5th globally.
The rural households were selected based on their economic status and the roof type of house. Roof type, along with wall and floor material, indicates the quality of houses and can be considered as an proxy indicator of socioecomic satus of a household32,33. The households were approached through local field staff- the Wasundhara Sevaks. Household members were informed about the study purpose after which consent was obtained via the household head. In the urban neighbourhoods of Delhi and Faisalabad, household heads were approached with support from the local community leaders. In Dhaka, residents appeared to be more accommodating and no mediatory support to gain household members’ trust was required. Urban households were selected based on two criteria; absence of any electric air-conditioning devices, and their location in selected low- and middle-income neighbourhoods. Air conditioning is generally related to higher socio-economic position in South Asia and often reported as an important socio-economic factor by which to classify vulnerable populations in heat stress studies34,35. The sampling of urban neighbourhoods was informed by a Local Climate Zone (LCZ) analysis in each city using Landsat images and spatial clustering21, with the final selection constrained by the practicalities of the research setup whereby indoor measurement locations had to be located near transects traversing these megacities (for details on the outdoor transect measurements, see Jacobs et al.24). While the indoor temperature and humidity data from various neighbourhoods can inform better heat warnings, the dataset does not have sufficient coverage to identify all particular areas of high or above average heat exposure across these cities. To design an effect early-warning system, a more elaborate observation campaign would be required.
Table 2 shows the descriptive statistics of indoor and outdoor temperature for each case study site. ‘Mean’, ‘min’ and ‘max’ were calculated by taking the mean of these respective values over all loggers in each site. ‘Min-min’(‘max-max’) is the absolute minimum (maximum) temperature measured indoors per site.
The demographic details of the households where indoor data loggers were installed are shown in Table 3. Family size is largerst in Faisalabad where extended families live in small two-rooms houses. Households in Delhi and Dhaka had about 50% more men than females, of working age, which is likely an effect of labour migration whereby the family stays behind in rural villages.
Heat stress was recognized as a health risk during the summer period in the majority of households in both urban and rural sites. Table 4 presents the top four perceived Heat Related Symptoms (HRS) and coping strategies by study sites. In the urban sites, feverish conditions/ undiagnosed fever is an often reported HRS followed by dehydration (including diarrhoea and vomiting). Tiredness and exhaustion was particularly often mentioned in Dhaka. Increased fluid intake, taking more showers and increased use of evaporatice coolers were viewed as key coping strategies. In rural sites, heavy sweating, leg cramps, thrist and fatigue are the most reported HRS, probably because people here are mostly engaged in outdoor activities during summer. Drinking more water, seeking shade, and covering the head when outdoors were key coping strategies reported.
The study design complied with all relevant international and national ethical regulations, having been approved by the International Development Research Centre (IDRC), Canada, whose ethics guidelines follow The 2nd edition of the Canadian Tri-Council Policy Statement on Ethical Conduct of Research Involving Humans. Informed consent was acquired from all research participants. Link to the ‘The 2nd edition of the Canadian Tri-Council Policy Statement on Ethical Conduct of Research Involving Humans’: https://publications.gc.ca/site/eng/381622/publication.html
With new technological developments, measuring indoor meteorological parameters without interfering with household activities has become much easier. Data loggers are miniaturised electronic devices used to measure indoor temperature and relative humidity. Here, HOBO UX 100-001 and HOBO UX100-011 data loggers were installed in houses within each study site. The indoor data loggers measured air temperature (0Celsius) (HOBO UX 100 001) and relative humidity (%) (HOBO UX100-011) with measurement intervals of 10 minutes.
The researchers and field staff installed these data loggers in the houses. In total, 206 temperature data loggers were installed across the study sites. Twenty of these loggers were able to measure relative humidity in addition to air temperature. In urban sites, six of these were installed to capture variations in humidity between different neighbourhoods, with an additional two installed in the rural study sites. Out of the initially installed data loggers, 169 remained in operation throughout the season and provided a time series of sufficient length. Some loggers stopped functioning, and in several cases occupants migrated. Others were considered faulty after the checking of the data, with records showing abnormal jumps in temperature possibly due to the logger being moved around. In few cases, loggers were thrown away due to mistrust by household members. Houses built in low-income neighbourhoods, especially in urban slums, often lack official status and house owners or renters treat outsiders with caution. In Faisalabad, Pakistan, particularly, concerns about the device being used for other purpose than temperature measurements had to be negotiated. Within the urban settings of Delhi, Dhaka and Faisalabad, indoor data loggers were installed in different neighborhoods, as shown in Table 5. In both rural areas, loggers were clustered in a single village.
For installing the data loggers, the research team followed a protocol, pre-tested in the Faisalabad study site, to minimise random measurement variations. The data loggers were installed either in the bedrooms or living rooms of households. In several cases, these two types of rooms were not distinguishable, as households with a lower socioeconomic background lack space. Some households even have the kitchen, bedroom and living room all in one room. In these houses, we installed the logger close to the sleeping corner. Otherwise, the decision where to install them was based on where household members spent most of their time. All loggers were fixed to a wall or a piece of furniture at approximately 1.3 m from the floor, away from any heat or cold sources, and from any solar radiation. Monthly to two-months visits were made to the houses to check on the loggers. During periodic field visits, temperature data were transferred to a laptop, checked and added to the database.
One AWS was installed in each of the five sites to determine the temporal evolution of the weather. An AWS is an assembly of various sensors to monitor various environmental parameters. The typical key sensors used in a weather station and collected in this study are air temperature, humidity, wind direction and speed (anemometer), global radiation, and evaporation. All AWS (Wireless Vantage Pro2 Plus or equivalent, Davis Instruments, USA) came with a small 5-watt solar panel which powered the system. These weather stations promise reliable operation without any manual intervention and the data can be accessed using the internet and a mobile application. All AWS were programmed to record data in an hourly interval.
The AWS stations were installed in an open space with sufficient distance from any physical structure to avoid direct shading, and away from large water bodies, industrial heat sources or high tension cables (both overhead and underground). In the two rural sites, the AWSs were placed close to the village, but at 300 m from the nearest building. In urban areas, buildings could not be avoided within a similar radius, but since our aim was to capture typical urban conditions, this was considered acceptable36. They were fenced for protection from humans, stray dogs and livestock. In Faisalabad, the AWS was installed at the campus of Government University College Faisalabad (GCUF), situated close to the city center. In Delhi, it was installed in front of The Energy and Resources Institute (TERI) University campus in South Delhi. In Dhaka, the AWS was installed close to the Bangladesh Meteorological Institute office building. In all the sites, prior permission for installation was obtained from the concerned authorities. GCUF and TERI were both project collaborators. All AWS stations were installed by experienced meteorologists following the user guidelines provided by the manufacturer. More detail on the AWS installation can be found in the supplement file (README FILE 4).
To relate indoor heat exposure with housing characteristics, data was collected on roof and wall material, roof and wall colour, the orientation of windows, doors and ventilation holes, room type and room height and presence of fans and evaporative coolers (Table 6). All houses are low-income housing types and are made of low cost and locally available materials, with some basic ventilation in the form of air holes, but hardly any specific insulation other than provided by the type of material itself which is indicated in the data tables, e.g. for walls and roofs. None of these houses had specific air sealing measures. Characteristics can be grouped into two; i. construction properties, such as roof and wall type; and ii. active and passive ventilation, e.g. ceiling fans or evaporative coolers, and the direction of ventilation and whether they were opened at night and closed during the day.
The main data-set is stored in a data repository as standalone datafiles (to access: https://doi.org/10.6084/m9.figshare.12546368.v1)37. The data can be categorised into three types i) indoor temperature and humidity data; ii) outdoor temperature data and other weather parameters, such as humidity, rainfall, solar radiation and wind speed and direction; iii) housing characteristics information. Indoor and outdoor temperature and humidity data is stored in.CSV file format (Comma-Separated Values). The housing characteristics can be found in the household data sheet (HSD) in a.CSV file format for each study site. In addition, the repository also contains a sample copy of the consent form.
In all houses, HOBO UX100-001/011 temperature data loggers from the Onset Corporation were installed. The temperature accuracy for these loggers is ± 0.21 K from 0° to 50 °C. After purchase, all loggers were validated in a climate chamber against a certified calibrated data logger. None of the loggers deviated more than ± 0.15 °C from the certified sensor. The accuracy of the loggers measuring relative humidity in addition to temperature, HOBO UX100-011, is ± 2.5% in a relative humidity range between 10% to 90% for humidity. The technical specifications of the data loggers are summarised in Table 7.
The following three steps ensured the technical validation and quality control of the data. First, the data loggers’ performance was checked after four to five days of installation to ensure that the data loggers were recording correctly. Second, in few cases, cross verification measurements of temperatures were taken during household interviews using a Kestrel-4600 handheld device. The handheld device can measure air temperature, wind speed, black globe temperature, and relative humidity. Every unit of this device is factory-tested for measurement accuracy and waterproof integrity. We did not find any difference between temperatures recorded by the handheld device and with the data loggers. Third, all data were downloaded from the data loggers into a laptop using the HOBO UX software and applying the unit in degree Celsius (°) for temperature and relative humidity (%) for humidity. Then the data were read out into.CSV format and merged into one.CSV file.
The station (Wireless Vantage Pro2 Plus, Davis Instruments, USA) includes solar radiation sensors and a daytime fan-aspirated radiation shield for temperature and humidity devices. Furthermore, wind speed and wind direction are measured using a cup anemometer and wind vane, respectively. The station is also equipped with a rain gauge and a barometer. All sensors measure at an interval of one minute and the readings are subsequently averaged or summed to obtain hourly values, with accuracies for wind speed 0.5 m s-1, air temperature 0.5 °C, relative humidity 2%, pressure 1hPa, rainfall 4% for rates up to 100 mm hr-1, solar radiation 5%. No household in the rural sites was more than 5 miles from the weather station. Urban households were within a 10 miles radius from the installed weather station.
The housing characteristics questionnaire was designed based on the research questions of the study project. To ensure that the questions are relevant and meaningful, pre-testing of the questionnaire (pre-coded and open-ended) was conducted in the study area through pilot surveys. After pre-testing, a revised tool was used for the data collection. During the survey, a researcher checked all the completed housing characteristics questionnaires for completeness (no missing values and units) and accuracy before they were submitted for data entry.
This dataset is anonymised and cannot be used to link data with individual study participants. All data (indoor and outdoor temperature) is stored into a.CSV file. It includes the actual readings from the data loggers and from the AWS station, in a cleaned and arranged format. We have also provided data supplement files (as README FILES) providing information on housing characteristics (README FILE 1), installation information on the indoor data loggers (README FILE 2), AWS parameters (README FILE 3) and AWS installation manual (README FILE 4). These supplemental files are available in a readme file format. The datasets can be used for indoor and outdoor temperature analysis for any region and/or to investigate urban-rural temperature variation. For example, there are a range of variables that will allow the user to examine factors that affect indoor temperature such as different roofing structures, wall structure and cooling devices. More information on the data format, labels and details can be obtained from a readme file provided in the data records link.
Users can download the indoor and outdoor temperature dataset and select the study areas (Jalna, Yavatmal, Delhi, Faisalabad and Dhaka) separately as per their analysis requirement. This dataset is complete and will not change later. In order to download data there is no need to take permission of the authors. As such, we encourage readers to use the data from the Figshare data repository.
As an illustration, we present a site-wise analysis of monthly average indoor-outdoor temperature variations (Fig. 2). Mean monthly temperatures, here clustered by roofing structure type, were obtained by aggregating temperature of 10-minute intervals into monthly average temperature. Mean monthly indoor temperatures are higher than temperatures outdoors, for all roof structure types. Indoor temperatures generally follow outdoor temperatures during the day, but houses cool down slower during the evening and night, so mean temperature indoors exceed those measured outdoors.
Monthly average indoor-outdoor temperature (°C).
The effect of housing characteristics differs per site and over the summer season. In Delhi, in summer, the highest monthly mean temperature was recorded in stone roof houses (34.5 °C). In houses with these types of roofs, indoor mean monthly temperatures are higher than the outdoor temperature during late summer, in May and June. In early summer, in April, the indoor temperature in tin roof houses (33.4 °C) is higher than outdoor temperature (32.8 °C). In Dhaka the highest monthly mean temperature was recorded in tin roof houses in the month of June (31.9 °C). The indoor temperature in tile roof houses was lower than in houses with a tin or concrete roof.
In Faisalabad, temperatures fluctuate strongly over the season, with the average highest outdoor temperature was recorded in June. Houses with a roof made of “concrete” slabs record the highest indoor temperatures, though not much different from those in houses with a single tile and double tile roofs houses. Poorer neigbourhoods in Faisalabad generally have few houses with tin roofs and none was included in our sample.
The indoor temperature observation in the rural site Yavatmal ranged from 36 °C to 38 °C in tin roof houses, while in concrete houses it was in the range between 34 °C to 36 °C. The monthly temperature variation in tin roof houses was higher by 3 °C to 4 °C than for outdoor temperature in May and June 2016. In the other rural study site, Jalna, the indoor temperature in thatch roof houses was lower (35.1 °C) than in concrete (36.8 °C) and tin roof (36.9 °C) houses. The recorded temperature shows that throughout the study period, the temperature in tin roof houses in rural areas was higher than in concrete roof houses, and even higher than the outdoor temperature. It is observed that when the outdoor temperature reaches its maximum, the low-mass corrugated metal roofs cool down rather quickly in the evenings compared to houses made out of concrete, whereas other roofs do not react similarly.
Figure 3 highlights the diurnal temperature variation for the five study sites. All sites except Dhaka, which has many overcast days during summer, show a strong diurnal pattern in termperatures, with daily maxima reaching up to or even over 40 °C both indoors and outdoors. In Delhi and Faisalabad, the ‘floor above’ houses are cooler than the outdoor. During noon, the indoor temperature in tin roofed houses (Yavatmal, Jalna, Delhi and Dhaka) is higher than in houses with other roof types. In Faisalabad, the average outdoor temperature is higher than all type of houses from 11 am to 6 pm. It is also observed that the outdoor temperature starts decreasing from 8 pm but the indoor temperature remains high. At night, indoor temperatures are generally higher than outdoor temperatures as heat is trapped inside the houses and within the buildup infrastructure in densily populated neighbourhoods.
Indoor-outdoor diurnal temperature variation for the summer months of May and June.
This study did not use any computer codes to generate the indoor and outdoor temperature dataset. Online, code is available to calculate various heat indices such as the Wet Bulb Globe Temperature (WBGT)38 based on the collected data.
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We would like to thank the International Development Research Centre (IDRC) for supporting with the Open Research Data Initiative (ORDI) project grant. The present data article was prepared under this ORDI project and it also covers the article publication cost. IDRC and the UK’s Department for International Development (DFID) funded the Collaborative Adaptation Research Initiative in Africa and Asia (CARIAA) program. The dataset for this paper was generated as part of the studies conducted under the CARIAA program. The Wageningen Environmental Research (WEnR), Team Climate Change WUR, the Netherlands provided technical guidance. We also thank The Energy and Resources Institute (TERI), Pakistan Agriculture Research Council (PARC), Government College University Faisalabad and Bangladesh Centre for Advance Studies (BCAS) for providing the indoor and outdoor temperature data for the urban sites. Last but not least, we would like to thank the respondents who have taken part in the research study and the field investigators who assisted in collecting data in all the study sites. Authors also thank the anonymous reviwers for there insightful comments on the earlier draft for this article.
WOTR Centre for Resilience Studies (W-CReS), Watershed Organisation Trust (WOTR), Pune, India
Premsagar Tasgaonkar & Dipak Zade
School of Social Work, Tata Institute of Social Sciences (TISS), Mumbai, India
Government College University Faisalabad, Faisalabad, Pakistan
The Energy and Resources Institute (TERI), Delhi, India
Department of Political Science and Institute of Behavioral Science - University of Colorado, Boulder, United States of America
Bangladesh Centre for Advanced Studies (BCAS), Dhaka, Bangladesh
Helmholtz Centre for Polar and Marine Research, Alfred Wegener Institute, Bremerhaven, Germany
Wageningen Environmental Research, Wageningen, Netherlands
Christian Siderius & Tanya Singh
Climate Change Research Centre, University of New South Wales, Sydney, Australia
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P.T. is principal investigator for the I.D.R.C. funded Open Research Data Initiative (ORDI) project. He analysed the indoor and outdoor temperature data for the rural sites of India and arranged all the data sets from the different study sites. P.T., D.Z., T.S. and C.S. were involved in study design, questionnaire preparation, data cleaning, analysis, and writing. S.E., G.G., N.M. and T.S. contributed towards collecting, arranging, and administrating the indoor and outdoor temperature dataset for Faisalabad (Pakistan), Delhi (India) and Dhaka (Bangladesh). T.S. also developed the housing characteristics questionnaire and helped in describing the data of the urban area study sites.
The authors declare no competing interests.
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Tasgaonkar, P., Zade, D., Ehsan, S. et al. Indoor heat measurement data from low-income households in rural and urban South Asia. Sci Data 9, 285 (2022). https://doi.org/10.1038/s41597-022-01314-5
DOI: https://doi.org/10.1038/s41597-022-01314-5
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