Abstract
Background
The impact of climate change on human health is not evenly distributed and is affected by regional geography and vulnerability of the local population. Official statistics that report these uneven impacts are needed to facilitate strategic planning and resource allocation.
Purpose
Identify globally defined indicators of the impacts of climate change on human health to inform the design of official statistics.
Methods
We followed recognized methods guidance for scoping reviews.
Results
Reviewing 4415 unique records, we extracted 73 unique and 33 repeated indicators from 20 sources. Temperature-related indicators were the most common (27%, 29/106), but many were repeated. Injury or illness indicators were more frequent than mortality indicators, with 59% (43/73) and 37% (27/73) respectively. Following breakdown of the categories into smaller, more specific outcomes, mortality from extreme weather events (n = 10) and illness due to zoonoses/vector-borne diseases (n = 9) were the most prevalent indicators. There was an absence/gap of indicators for five secondary categories.
Conclusion
Synthesis of climate-sensitive health indicators is crucial for establishing a cohesive official statistics framework to monitor the health impacts of climate change-related events. The abundance (and gaps) of indicators across categories of health effects aids in prioritization of developing new indicators and improving data availability.
Keywords: climate change, official statistics, health indicators
1. Introduction
Official statistics have a vital role in supporting risk assessment and decision-making by government, business, civil society organizations, researchers and members of the public. 1 One area of urgent and increasing concern for the development and application of official statistics and indicators is climate change. 2 Strong climate change action requires support from sophisticated statistical frameworks with comprehensive indicators. Indicators, with their potential to reveal relative positions or show positive or negative change, are crucial for setting targets and monitoring achievement.1,2
Given the large magnitude of human health impacts of climate change, 3 corresponding official statistics and related data infrastructure to monitor prevalence and temporal changes are required. Data must be robust enough to meet the following decision-making challenges: the need to consider decisions and their impacts over multiple overlapping time-scales; the inherent uncertainty in the rate, magnitude and pattern of climate change for any one location; and the fact that relevant data may be unavailable, or imprecise, especially at the local scale at which many health-system decisions are made.4,5
Health-system decision makers are progressively becoming aware that climate change poses increasing threats to human health. Climate change leads to increasing levels of carbon dioxide and short-lived climate pollutants; rising temperatures; rising sea levels; and increases in the intensity, frequency, duration and seasonality of extreme weather events. 6 Related health impacts can be direct; for example, extreme heat disproportionately affects certain population groups, such as young children, the elderly, and those living in substandard housing or who are unhoused.7,8 The impacts may also be indirect, with delivery of quality care and health facility infrastructure being impaired by a changing climate. For example, extreme weather events have particular impacts on people whose health depends on regularly scheduled and uninterrupted access to health services and those with technology dependencies. 9 Monitoring human health impact and risk from climate change requires reliable, long-term data sets. 10
Recognizing the need to support decision-making in this complex and important area, inter-governmental organizations such as the World Health Organization (WHO) and research teams, notably the Lancet Countdown collaboration, have developed indicators for climate-health outcomes. This review supports the Official Statistics on Climate-Health Interactions (SOSCHI) project, led by the UK Office for National Statistics and funded by Wellcome. 11 The goal of SOSCHI is to develop a transparent, globally generalizable, and spatially scalable (from national to regional) framework and technical platform for official statistics on climate change, the environment, and health. 11 The partners on the SOSCHI project include the African Institute for Mathematical Sciences (AIMS) Rwanda, the Regional Institute for Population Studies (RIPS) at the University of Ghana, the UK Health Security Agency and the Cochrane Planetary Health Thematic Group. 11 This project will develop methods and tools that can be applied by analysts across a broad range of contexts, to produce regular indicators that can inform policy and practice. The outputs of the project will help stakeholders produce high-quality data and statistics and communicate with a range of audiences. 11
To support the development of a unified indicator set, the scoping review reported in this article was undertaken by staff from the Cochrane Planetary Health Thematic Group, working closely with the ONS, to collate published indicators and statistical approaches that measure the impact of climate change on human health. The primary research question this scoping review aims to address is, what indicator sets or statistical approaches have already been published for climate-health related data?
2. Methods
Our preliminary scan of relevant literature revealed that mapping the available indicator sets would require collating information from a wide range of evidence types. Therefore, we used a scoping review methodology. This approach is suitable for examining the extent, range, and nature of research activity in a particular area, summarizing, and disseminating research findings, and identifying gaps in the available literature. Similar to a systematic review, a scoping review uses systematic and rigorous methods to collate and present the research evidence relevant to a particular question. In contrast to a systematic review, however, a scoping review addresses a broad topic for which many study designs may be applicable and does not include quality assessment of included studies. A scoping review approach is highly suitable for a broad area that has not been previously mapped, as is the case with the current state of global climate-health indicators. This scoping review was guided by the methodology framework outlined by Arksey and O’Malley and the more recent PRISMA extension for scoping reviews.12,13 The protocol was registered in Open Science Framework (https://osf.io/swx9h/).
2.1. Inclusion criteria
Documents included in this scoping review discuss or report the use of globally defined indicators for health outcomes in the context of climate change. For this project, globally defined indicators were defined as having the following characteristics:
A quantitative, comparable measure of a health outcome or health status (i.e., mortality, illness, hospitalizations, emergency department presentations). Indicators reporting vulnerability or exposure were excluded.
Directly linked, or having some level of attribution, to climate change or climate change-related events as reported by the authors.
Contained in a document for which at least one author reports an affiliation with, or the indicator is used by centers recognized as, global health authorities.
The definition of global authority was developed with input from multiple stakeholders. A global authority needed to have a worldwide scope or represent a consortium of multiple countries such as the European Union. National organizations from the United States (US) such as the US Centers for Disease Control (CDC) and the US Environmental Protection Agency (EPA) were included due to the significant impact and uptake of their work globally. Evidence syntheses (systematic, scoping and narrative reviews) were included as well as white papers, reports, position statements/recommendations, policies, working group reports, and frameworks from global health authorities. Primary research articles (observational studies, RCTs, case reports, case series) that described an association between climate change and a specific health outcome, but not how to measure that association, were excluded. Also excluded were letters, opinion pieces, abstracts and clinical guidelines.
2.2. Search strategy
The comprehensive database search strategy was developed by an information specialist in consultation with project members from the UK Office for National Statistics (ONS) and the Cochrane Planetary Health Thematic Group (CPHTG). The strategy was based on the concepts of climate change and health indicators using key words such as climate change, global warming, environmental health, health, health status, indicator, measure, metric, and statistic. The search was executed in the following biomedical databases from inception to May 2023: EBSCO, Embase, Epistemonikos, MEDLINE, ProQuest, Google Scholar, Elsevier Scopus, Clarivate Web of Science. The full search strategy is available in Appendix A.
An additional search of grey literature was also undertaken through systematic screening of relevant websites of accepted global authorities on climate change and human health. The websites were identified by the ONS and CPHTG members and included the National Institutes of Health (NIH) Climate Change and Human Health Literature Portal, the WHO, the CDC, the United Nations (UN) and the European Environment Agency (EEA Climate-ADAPT) (see Appendix B for the complete list). Each website was reviewed independently by two review authors for relevant page titles and those with built-in search engines were searched using synonyms and different configurations of the text words “indicator,” “health” and “climate change.”
2.3. Evidence selection
Records identified by the database search were de-duplicated and uploaded into the COVIDENCE tool (Veritas Health Innovation). Two review authors screened at the title and abstract level following a small (n = 20) pilot screening to ensure consistency. Following the first level screening, potentially relevant publications were subject to a further round of independent screening at the full text level by the same two review authors. Any disagreements were resolved by consensus or consultation with a third author.
Records identified by the website search were recorded in Excel (Microsoft). Documents available in PDF were added to the COVIDENCE tool at the full text level. Information available only on a website underwent additional full screening using Excel to track decisions. Any disagreements were resolved by consensus or consultation with a third author.
2.4. Data extraction
Data were extracted independently by two review authors using a pilot-tested Excel spreadsheet. All data variables were pre-defined in an extraction code book to ensure consistency. In addition to basic descriptive data, key information extracted included the name of the indicator, the verbatim definition of the indicator, spatial scale (global, national, regional), data source, and the authors’ determination of the indicator's proximal or distal linkage to climate change. Any disagreements were resolved by consensus or consultation with a third author.
2.5. Analysis of evidence
Categorization
Measures of climate-sensitive health outcomes identified were sorted into eight primary categories based on climate change impacts on health illustrated by the WHO (Table 1).6,14 Categorization was undertaken independently by two review authors. Any indicators that fit in more than one category were classified under the most relevant outcome as determined by the reviewers. For example, the indicator ‘number of cases of Giardiasis’: Giardiasis is mainly a water-borne disease but can also be food-borne; based on the above sorting methods this indicator was classified as water-borne.
Table 1.
Primary categories of climate change related health outcomes.
| • Extreme weather event-related injury and mortality | • Zoonoses & vector-borne diseases |
| • Temperature-related illness and mortality | • Malnutrition and food-borne diseases |
| • Air quality-related illness and mortality | • Mental and psychosocial health |
| • Water-borne diseases and other water-related health impacts | • Other (e.g., non-communicable diseases) |
Secondary categorization of the indicators involved breaking down each primary category into smaller, more specific outcomes based on the measure (e.g., mortality vs illness) or other identifiers. Examples are shown in Table 2; the full list can be found in Figure 4.
Table 2.
Examples of secondary category development
| Primary category | Secondary categories | |
|---|---|---|
| Extreme weather event-related injury and mortality | Injury due to extreme weather events | Mortality due to extreme weather events |
| Temperature-related illness and mortality | Heat-related illness | Heat-related mortality |
| Cold-related illness | Cold-related mortality | |
Figure 4.

Frequency of unique indicators in each secondary category.
Unique indicators
To determine if an indicator was unique, the review authors examined both the indicator name and reported definition. Indicators with similar names and definitions were grouped together under one unique indicator (e.g., heat-related mortality and deaths from extreme heat would fall under one unique indicator). When this occurred the most straightforward indicator name would be used as the unique indicator title while the remaining similar indicators were referred to as repeated indicators. All the distinct definitions for the indicators were retained for the description. Indicators were not separated into unique categories based on location (e.g., the indicators ‘flood-related deaths in Europe’ and ‘flood-related deaths in the US’ would both be listed under the unique indicator ‘flood-related deaths’), or on units of measurement (e.g., the indicators ‘total number of deaths from heat’ and ‘death rate per 100,000 due to heat’) would both be listed under the indicator ‘heat-related mortality’.
3. Results
From both the database and website searches 4415 unique records were screened at the title and abstract level; 154 underwent further full text screening and 73 unique indicators and 33 repeated indicators were extracted from 23 publications (20 papers and 3 websites totalling 13 pages). Figure 1 illustrates the flow of sources through the inclusion process. Three of the papers were part of the Lancet Countdown's ongoing publications of climate change indicators and reported duplicate or out-of-date indicators. These three papers were excluded from the analysis, leaving a total of 17 papers. Table 3 summarizes the characteristics of included studies. Sources that were excluded based on our definition of global authority are available in Appendix C.
Figure 1.

PRISMA diagramn.
Table 3.
Characteristics of included studies.
| First | Global | ||||
|---|---|---|---|---|---|
| Author, | Data | Climate change health | organization or | How data were | |
| Year | origin | indicator categories addressed | author affiliation | identified/synthesized | Data sources |
| Berko 2014 15 | USA | Extreme weather-related injury and mortality, Temperature-related illness and mortality | CDC | Vital statistics were used to measure weather-related health events | National Center for Health Statistics |
| Bernard 2001 16 | USA | Air quality-related illness and mortality | CDC, US EPA | Health effects for indicators obtained from an American Thoracic Society review based on extensive evidence drawn from animal and in vitro toxicology, human clinical exposure studies, field exposure studies, and epidemiologic studies. | US EPA |
| CDC's Climate and Health Program (2023 Website) 17 | USA | Temperature-related illness and mortality | CDC's Climate and Health Program | Indicators were developed in collaboration with national, state, and local environmental health partners. ‡ | National Syndromic Surveillance Program, Government bureau department data |
| CSTE 2018 18 | USA | Extreme weather-related injury and mortality, Temperature-related illness and mortality, Air quality-related illness and mortality, Zoonoses & vector-borne diseases | CDC | Development of the indicators included a comprehensive literature review, identification of longitudinal data sets that were applicable at the state and community level, and pilot studies to improve and finalize implementation instructions. ‡ | Statewide hospital discharge records, SHELDUS, CDC Lyme Stats tables and Statewide Data |
| Dora 2015 19 | 90 countries | Air quality-related illness and mortality, Malnutrition and food-borne diseases | WHO | Indicators were identified through a process of scoping review and expert and stakeholder consultation | WHO Global Household Air Pollution Measurement database and WHO indoor air quality guidelines |
| English 2009 20 | USA | Extreme weather-related injury and mortality, Temperature-related illness and mortality, Air quality-related illness and mortality, Zoonoses & vector-borne diseases, Malnutrition and food-borne diseases | CDC, US EPA | Indicators selected following review of governmental and nongovernmental documents and published literature ‡ | National Center for Health Statistics, EM-DAT, ArboNET surveillance system, CDC Division of Vector-borne Infectious Diseases |
| European Climate and Health Observatory – Climate ADAPT (2022 Website) 21 | Europe | Extreme weather-related injury and mortality, Temperature-related illness and mortality | European Climate and Health Observatory, Climate ADAPT | Indicators drawn from Lancet Countdown and Copernicus Climate Change Service ‡ | ERA5-Land, EURO-CORDEX, Copernicus Climate Change Service, Copernicus Atmosphere Monitoring Service, Lancet Countdown, CATDAT |
| European Environment Agency (2016 Website) 22 | Europe | Extreme weather-related injury and mortality | EEA | NR ‡ | WHO, Eurostat, EM-DAT |
| European Environment Agency 2022 23 | Europe | Temperature-related illness and mortality, Water-borne diseases and other water-related health impacts, Zoonoses & vector-borne diseases, Malnutrition and food-borne diseases | EEA | Indicators drawn from Lancet Countdown in Europe and Copernicus Climate Change Service, as well as case studies throughout Europe and national policy analyses | European Centre for Disease Control and Prevention database |
| Jung 2018 24 | Western Pacific | Extreme weather-related injury and mortality, Zoonoses & vector-borne diseases, Malnutrition and food-borne diseases | WHO (Western Pacific Region) | United Nations Sustainable Development Goals used as framework | World Bank Data Bank |
| Lay 2018 25 | USA | Temperature-related illness and mortality | CDC, US EPA | Used ICD codes to measure temperature-related health events ‡ | Truven Health Research database, North American Land Data Assimilation System |
| Romanello 2022 26 | Global | Extreme weather-related injury and mortality, Temperature-related illness and mortality, Air quality-related illness and mortality | Lancet Countdown, UN | Indicators selected following international collaboration and consensus ‡ | European Centre for Medium-range Weather Forecasts, EM-DAT, Human Development Index at the UN Development Programme |
| Swedish International Development Cooperation Agency (SIDA) 2011 27 | Global | Extreme weather-related injury and mortality, Zoonoses & vector-borne diseases, Malnutrition and food-borne diseases | SIDA | Indicators selected from those in use by partner countries and internationally accepted ones | Commission for Sustainable Development, Millennium Development Goals, Joint Monitoring Programme, WHO, EM-DAT |
| United Nations Economic and Social Commission for Western Asia 2017 28 | Middle East | Extreme weather-related injury and mortality, Temperature-related illness and mortality, Water-borne diseases and other water-related health impacts, Zoonoses & vector-borne diseases | UN ESCWA | Proposed indicators were discussed at expert group meeting, from which final indicators were selected | UNISDR, Global Health Data Exchange |
| United States Environmental Protection Agency 2016 29 | USA | Temperature-related illness and mortality, Zoonoses & vector-borne diseases | US EPA | Indicators screened and selected based on usefulness, data quality, and relevance from peer-reviewed, publicly available data ‡ | CDC National Vital Statistics system and Environmental Public Health Tracking Program |
| Van Daalen 2022 30 | Europe | Temperature-related illness and mortality | Lancet Countdown, UN | Indicators selected following international collaboration and consensus ‡ | Eurostat, European Centre for Medium-range Weather Forecasts, Geostat |
| World Health Organization 2018 31 | Global | Extreme weather-related injury and mortality | WHO | Indicator selection guided by priority global monitoring requirements related to human health, with organizations such as the UN and World Health Assembly ‡ | Ministries of Health, National Disaster Loss Database |
| World Health Organization 2020 32 | Global | Air quality-related illness and mortality, Water-borne diseases and other water-related health impacts, Zoonoses & vector-borne diseases | WHO | A draft global strategy, including climate change elements, was submitted to WHO's regional committees and Executive Board | NR |
| World Meteorology Organization 2021 33 | Global | Extreme weather-related injury and mortality, Temperature-related illness and mortality | WMO | NR | EM-DAT |
| Zhang 2018 34 | Western Pacific | Extreme weather-related injury and mortality, Temperature-related illness and mortality, Mental and psychosocial health | Lancet Countdown, UN | Lancet Countdown indicators were assessed in the Australian context ‡ | EM-DAT |
‡ Detailed statistical methods are reported.
Three of the analyzed sources were from the Lancet Countdown (one each from the Global Countdown, 26 the European Countdown, 30 and the Australian Countdown. 34 The organizations producing or associated with the rest of the sources were: the US CDC (n = 6),15–18,20,25 the WHO (n = 4),19,24,31,32 the US EPA (n = 4),16,20,25,29 the United Nations (UN) (n = 3),26,30,34 the European Environmental Agency (n = 2),22,23 the European Climate and Health Observatory (n = 1), 21 the Swedish International Development Agency (SIDA) (n = 1),27 the UN Economic and Social Commission for Western Asia (ESCWA) (n = 1), 28 and the World Meteorological Organization (WMO) (n = 1). 33 Some sources had more than one global affiliation. The papers were published between 2001 and 2023 with the majority (85%, n = 17) published after 2014.
3.1. Primary categorization
From the 20 analyzed sources, 106 indicators were extracted and sorted into primary categories (Table 1), allocating one category per indicator. Nine indicators initially fit into more than one primary category. For the categories listed in Table 1, indicators for temperature-related illness and mortality were most frequent (27%, n = 29/106), followed by indicators for extreme weather event-related injury and mortality (22%, n = 23/106) and air quality-related illness and mortality (20%, n = 21/106) (Figure 2). No indicators were extracted for the category of ‘Other outcomes (e.g., non-communicable diseases)’.
Figure 2.

Frequency of indicators in each primary category.
Dark boxes represent the number of unique indicators for that primary health outcome category (n = 73). Light boxes represent repeated indicators (n = 33).
3.2. Unique indicators
Seventy-three indicators were identified as unique and are listed along with all their reported definitions in Table 4, organized by primary category. The largest number of unique indicators was found for the health outcomes of air quality-related illness and mortality (28%, n = 29/73), followed by indicators for extreme weather event-related injury and mortality (19%, n = 14/73) and temperature-related illness and mortality (16%, n = 12/73) (Figure 2). Four of the primary categories contained only unique indicators (mental and psychosocial health, water-borne diseases and other water-related health impacts, malnutrition and food-borne diseases, and air quality-related illness and mortality), while the remaining three had a range of 7 to 17 repeated indicators (zoonoses & vector-borne diseases (n = 7), extreme weather event-related injury and mortality (n = 9) and temperature-related illness and mortality (n = 17) (Figure 2). Regarding health outcome severity, for all categories unique indicators measuring injury or illness were most frequent (59%, n = 43/73) compared to indicators measuring mortality (37%, n = 27/73) or measuring both mortality and morbidity (4%, n = 3/73) (Figure 3).
Table 4.
List of unique indicators (n = 73) and related indicators (n = 33) for climate change impacts on human health, grouped by primary category.
| Related Indicators | Global organization | |||
|---|---|---|---|---|
| Unique Indicator | (if applicable) | Definition | or author affiliation | Data origin |
| Extreme weather event-related injury and mortality | ||||
| All weather-related deaths | Not applicable | Deaths due to weather (extreme natural heat, extreme natural cold, floods, storms, and lightning) may be identified by using both the underlying and contributing causes of death. | CDC | USA |
| Flood-storm-lightning-related deaths | Not applicable | Flood-storm ICD–10 codes X38 (victim of flood), X37 (victim of cataclysmic storm), or X33 (victim of lightning) on death certificate. | CDC | USA |
| Total number of victims (killed or affected) of natural disasters (women/men) | Not applicable | Measures total numbers of victims killed or affected by natural disaster and is thus an indicator for vulnerability to natural disasters, including geophysical, hydrological meteorological, climatological, and biological disasters. In case of limited disaster preparedness and weak resilience more people will be affected. | SIDA | Global |
| Number of deaths, missing persons, and directly affected persons attributed to disasters per 100,000 population | Number of deaths, missing persons, and directly affected persons attributed to disasters per 100,000 population. | WHO | Western Pacific | |
| Deaths due to drought | Not applicable | Numbers of reported deaths due to drought from 1970–2019. | WMO | Global |
| Deaths due to storms | Not applicable | Numbers of reported deaths due to storms from 1970–2019. | WMO | Global |
| Deaths due to flood | Not applicable | Numbers of reported deaths due to flood from 1970–2019. | WMO | Global |
| Fatalities associated with floods | Number of fatalities associated with floods. | European Climate and Health Observatory Climate ADAPT | Europe | |
| Deaths related to flooding in Europe | Deaths per million inhabitants related to flooding in Europe. | EEA | Europe | |
| Number of reported deaths due to landslide | Not applicable | Number of reported deaths due to landslide from 1970–2019. | WMO | Global |
| Number of reported deaths due to wildfire | Not applicable | Number of reported deaths due to wildfire from 1970–2019. | WMO | Global |
| Fatalities associated with wildfires | Number of fatalities associated with wildfires. | European Climate and Health Observatory Climate ADAPT | Europe | |
| Deaths due to extreme weather events | Not applicable | Deaths (per 100,000 population) from wildfires, flooding, and storms. | CDC | USA |
| Lethality of extreme weather events | Deaths, as proxy of the lethality of weather-related disasters, are defined as the number of people who lost their life because the disaster happened. | Lancet Countdown, UN | Global | |
| Number of mortalities from extreme weather events | Number of mortalities from extreme weather events (flooding and storms). | CDC, US EPA | USA | |
| Number of deaths attributed to disasters | Number of people who died during the disaster, or directly after, as a direct result of the hazardous event. | WHO | Global | |
| Number of deaths attributed to hydrometeorological disasters | Not applicable | This indicator measures the number of people who died during the disaster, or directly after, as a direct result of the hazardous event (per 100,00 population). | UN ESCWA | Middle East |
| Number of missing persons attributed to hydrometeorological disasters | Not applicable | Missing: The number of people whose whereabouts is unknown since the hazardous event. It includes people who are presumed dead although there is no physical evidence (per 100,000 population). | UN ESCWA | Middle East |
| Number of missing persons by disaster per 100,000 people | Missing: number of people whose whereabouts is unknown since the hazardous event. It includes people who are presumed dead although there is no physical evidence. The data on number of deaths and number of missing are mutually exclusive. | WMO | Global | |
| Injuries due to extreme weather events | Not applicable | Injuries (per 100,000 population) from wildfires, flooding, and storms. | CDC | USA |
| Number of injuries from extreme weather events | Number of injuries from extreme weather events. | CDC, US EPA | USA | |
| People affected by weather-related disasters | Not applicable | People affected are defined as those requiring immediate assistance during a period of emergency; hence requiring basic survival needs such as food, water, shelter, sanitation and immediate medical assistance. | Lancet Countdown, UN | Global |
| Lethality of weather-related disasters | Not applicable | Died from drought, floods, storms, bushfires and extreme temperature. | Lancet, UN | Western Pacific |
| Temperature-related illness and mortality | ||||
| Heat-related deaths | Not applicable | ICD–10 codes X30 (exposure to excessive natural heat), T67 (heatstroke or sunstroke), or both on death certificate. | CDC | USA |
| Heat related deaths | Annual rate for deaths classified by medical professionals as “heat-related” each year in the United States. | US EPA | USA | |
| Deaths due to extreme temperature | Numbers of reported deaths due to extreme temperature from 1970–2019. | WMO | Global | |
| Number of heat-related deaths | This indicator measures the annual number of deaths attributable to high temperatures. | UN ESCWA | Middle East | |
| Heat-related mortality | Annual deaths per million inhabitants. | EEA | Europe | |
| Heat-related mortality | Heat-related mortality | Lancet | Europe | |
| Health effects of temperature change | Association between summer daily mean temperature and non-accidental mortality. | Lancet | Western Pacific | |
| Summer heat-related mortality | Heat death: ICD-10 codes X30 or T67.0 – T67.9, EXCLUDING cases having ICD-10 code W92 (man-made source of heat) in any cause of death from May through September. | CDC | USA | |
| Heat-related mortality | Heat-related mortality incidence (annual deaths per million inhabitants) in Europe. | European Climate and Health Observatory Climate ADAPT | Europe | |
| Excess mortality due to extreme heat | Death as heat-related when heat is the underlying or contributing cause of death. Excess mortality can be calculated by comparing the number of deaths during an extreme temperature event with those during a reference period that has been matched by day of the week and other potentially confounding factors, or by using a time-series approach. | CDC, US EPA | USA | |
| Deaths due to heat and cardiovascular disease | Not applicable | heat-related cardiovascular disease deaths, which include deaths due to heart attacks, strokes, and other diseases related to the circulatory system. | US EPA | USA |
| Heat-related deaths | Deaths result from heat stroke and related conditions, cardiovascular disease, respiratory disease, and cerebrovascular disease. | CDC's Climate and Health Program | USA | |
| Heat-related mortality (over 65) | Not applicable | Global heat-related mortality for populations older than 65 years. | European Climate and Health Observatory Climate ADAPT | Europe |
| Heat-related mortality | Tracks the global total number and spatial pattern of heat-related mortality from 2000 to 2019 of the 65-and-older population. | Lancet Countdown, UN | Global | |
| Health effects of temperature change | Not applicable | Association between summer daily mean temperature and non-accidental mortality | Lancet | Western Pacific |
| Cold-related deaths | Not applicable | ICD–10 codes X31 (exposure to excessive natural cold), T68 (hypothermia), or both on death certificate. | CDC | USA |
| Hyperthermia emergency department (ED) visits | Not applicable | (ICD9-CM codes 992.0–992.9). | CDC, US EPA | USA |
| Emergency department (ED) visits associated with heat-related illness (HRI) | Not applicable | Emergency department (ED) visits associated with heat-related illness (HRI) per 100,000 ED visits. | CDC's Climate and Health Program | USA |
| Summer heat-related morbidity -ED visits | ED visits due to heat. From May 1, 2000 to September 30, 2015 use ICD-9-CM codes (992.0 to 992.9, E900.0, E900.9). From May 1, 2016 to present, use ICD-10-CM codes (X30, T67.0-T67.9). | CDC | USA | |
| Cardiovascular emergency department (ED) visits | Not applicable | ICD9-CM codes 460–519. | CDC, US EPA | USA |
| Myocardial infarction (MI) emergency department (ED) visits | Not applicable | ICD9-CM code 410. | CDC, US EPA | USA |
| Heat-related hospitalizations | Not applicable | Rates for hospital admissions due to “heat-related” illnesses such as heat exhaustion, heat cramps, mild heat edema (swelling in the legs and hands), heat syncope (fainting), and heat stroke. It is based on hospital discharge records, which include a diagnosis determined by a physician or other medical professional (per 100,000 people). | US EPA | USA |
| Summer heat-related morbidity- hospitalizations | Hospitalizations due to heat. From May 1, 2000 to September 30, 2015 use ICD-9-CM codes (992.0 to 992.9, E900.0, E900.9). From May 1, 2016 to present, use ICD-10-CM codes (X30, T67.0-T67.9). | CDC | USA | |
| Heat-related illness | Not applicable | Includes cardiovascular and respiratory complications, renal failure, electrolyte imbalance, kidney stones, negative impacts on fetal health, and preterm birth. | CDC's Climate and Health Program | USA |
| Excess morbidity due to extreme heat | Excess morbidity due to extreme heat. | CDC, US EPA | USA | |
| Annual worker heat-related illness cases with days away from work | Not applicable | Annual worker heat-related illness cases with days away from work. | CDC's Climate and Health Program | USA |
| Annual rate of heat-related illness with days away from work per 10,000 full-time workers | Annual rate of heat-related illness with days away from work per 10,000 full-time workers. | CDC's Climate and Health Program | USA | |
| Annual worker days lost due to heat-related illness | Not applicable | Annual worker days lost due to heat-related illness. | CDC's Climate and Health Program | USA |
| Annual median days of work lost due to heat-related illness | Annual median days of work lost due to heat-related illness. | CDC's Climate and Health Program | USA | |
| Air quality-related illness and mortality | ||||
| Premature cardiorespiratory mortality | Not applicable | Deaths from heart or lung disease in excess of number expected. | CDC, US EPA | USA |
| Increased health care use | Not applicable | Increased hospitalizations, physician visits, emergency department visits. | CDC, US EPA | USA |
| Asthma exacerbations | Not applicable | Increased physician and emergency department visits, medication use, symptom reporting. Decreased peak flow measurements. | CDC, US EPA | USA |
| Increased respiratory illness | Not applicable | Increased respiratory infections, physician visits, episodic symptoms. | CDC, US EPA | USA |
| Mortality rate attributed to household and ambient air pollution | Not applicable | Mortality rate attributed to household and ambient air pollution. | WHO | Global |
| Estimated burden of disease from urban ambient air pollution | Not applicable | Estimates of burden of disease from ambient air pollution in cities are generated by WHO air quality data (from monitoring of stations, satellite remote sensing, and air pollution chemical transport models) and scientific evidence from population exposure–response relationships. | WHO | Global |
| Mortality attributed to household air pollution | Not applicable | Modelled estimates of personal household air pollution exposure from the WHO Global Household Air Pollution Measurement database and WHO indoor air quality guidelines for household fuel combustion, which summarises evidence from exposure-response studies. | WHO | Global |
| Morbidity attributed to household air pollution | Not applicable | Modelled estimates of personal household air pollution exposure from the WHO Global Household Air Pollution Measurement database and WHO indoor air quality guidelines for household fuel combustion, which summarises evidence from exposure-response studies. | WHO | Global |
| Global mortality attributed to outdoorambient air pollution at levels above WHO guidelines (annualmean PM 2·5 or 10 μg/m³). | Not applicable | Population exposure to ambient air pollution concentrations exceeding WHO Air Quality Guidelines based on ground level urban air pollution monitoring of data collected by WHO and complemented by other methods such as remote sensing using satellite data and air pollution (chemical) transport models, to cover areas with little data. Mortality estimates based on population exposure to air pollution from monitoring of data in association with evidence on exposure-response, as summarised in WHO Air Quality Guidelines. | WHO | Global |
| Global morbidity attributed to outdoorambient air pollution at levels above WHO guidelines (annualmean PM 2·5 or 10 μg/m³). | Not applicable | Population exposure to ambient air pollution concentrations exceeding WHO Air Quality Guidelines based on ground level urban air pollution monitoring of data collected by WHO and complemented by other methods such as remote sensing using satellite data and air pollution (chemical) transport models, to cover areas with little data. Morbidity estimates based on population exposure to air pollution from monitoring of data in association with evidence on exposure-response, as summarised in WHO Air Quality Guidelines. | WHO | Global |
| Mortality from ambient air pollution by sector | Not applicable | This indicator estimates the mortality attributable to ambient PM2·5, combining atmospheric modelling with information about activity in emitting sectors. | Lancet Countdown, UN | Global |
| Premature deaths from ambient PM 2.5 exposure due to electricity use for air conditioning | Not applicable | To estimate country/region-specific premature deaths from ambient PM 2.5 exposure due to electricity use for air conditioning the proportion of total electricity final consumption used for air conditioning was multiplied by the estimated country/region-specific premature deaths due to PM 2.5 emissions from electric power plants. | Lancet Countdown, UN | Global |
| Asthma related hospital admissions | Not applicable | The number of hospitalization for the following disease groups by stratifying data: a. Asthma (493 or J45). Number and rate per 100,000 population | CDC | USA |
| Asthma related ED visits | Not applicable | Principal (primary) discharge diagnosis:a. Asthma (493 or J45). Number and rate per 100,000 population | CDC | USA |
| Allergic disease related hospital admissions | Not applicable | The number of hospitalization for the following disease groups by stratifying data:a. Allergic rhinitis (hay fever) (477 or J30.1)b. Atopic dermatitis (eczema) (691.8 or L20)c. Allergic urticaria (hives) (708.0 or L50.0)d. Allergic conjunctivitis (372.14 or H10.1). Number and rate per 100,000 population | CDC | USA |
| Allergic disease related ED visits | Not applicable | Principal (primary) discharge diagnosis:a. Allergic rhinitis (hay fever) (477 or J30.1)b. Atopic dermatitis (eczema) (691.8 or L20)c. Allergic urticaria (hives) (708.0 or L50.0)d. Allergic conjunctivitis (372.14 or H10.1). Number and rate per 100,000 population | CDC | USA |
| Human cases of coccidioidomycosis | Not applicable | Human cases of coccidioidomycosis. | CDC, US EPA | USA |
| Respiratory/allergic disease related to increased air pollution | Not applicable | Respiratory/allergic disease related to increased air pollution (O3 and other pollutants). | CDC, US EPA | USA |
| Respiratory/allergic mortality related to increased air pollution | Not applicable | Respiratory/allergic disease related to increased air pollution (O3 and other pollutants). | CDC, US EPA | USA |
| Respiratory/allergic disease related to increased pollens | Not applicable | Respiratory/allergic disease related to increased pollens. | CDC, US EPA | USA |
| Respiratory/allergic mortality related to increased pollens | Not applicable | Respiratory/allergic mortality related to increased pollens. | CDC, US EPA | USA |
| Water-borne diseases and other water-related health impacts | ||||
| [Cases of] Leptospirosis | Not applicable | Confirmed cases per 100,000 population. | EEA | Europe |
| [Cases of] Shigellosis | Not applicable | Confirmed cases per 100,000 population. | EEA | Europe |
| [Cases of] Cryptosporidiosis | Not applicable | Confirmed cases per 100,000 population. | EEA | Europe |
| [Cases of] Giardiasis | Not applicable | Confirmed cases per 100,000 population. | EEA | Europe |
| Mortality rate attributed to unsafe water, unsafe sanitation and lack of hygiene (exposure to unsafe Water, Sanitation and Hygiene for All (WASH) services | Not applicable | Mortality rate attributed to unsafe water, unsafe sanitation and lack of hygiene (exposure to unsafe Water, Sanitation and Hygiene for All (WASH) services. | WHO | Global |
| Incidence of waterborne diseases | Not applicable | Incidence of waterborne diseases. | UN ESCWA | Middle East |
| [Cases of] Legionnaires’ disease | Not applicable | Confirmed cases per 100,000 population. | EEA | Europe |
| Zoonoses & vector-borne diseases | ||||
| Mortality from climate-sensitive diseases | Not applicable | Mortality from climate-sensitive diseases. | WHO | Global |
| Incidence of vector-borne and waterborne diseases | Not applicable | This indicator tracks the annual incidence of vector- borne diseases (number of cases). | UN ESCWA | Middle East |
| Deaths among children under five years of age due to malaria (%) (girls/boys) | Not applicable | Measures the share of children under five years of age that die, where malaria is the underlying cause of death. Underlying cause-of-death information is needed. | SIDA | Global |
| Dengue infections | Not applicable | Confirmed cases per 100,000 population. | EEA | Europe |
| Human cases of dengue fever | Human cases of dengue fever. | CDC, US EPA | USA | |
| Malaria incidence | Not applicable | Malaria incidence per 1000 population. | WHO | Global |
| [Cases of] Malaria | Confirmed cases per 100,000 population. | EEA | Europe | |
| [Cases of] Chikungunya | Not applicable | Confirmed cases per 100,000 population. | EEA | Europe |
| [Cases of] Tick-borne encephalitis | Not applicable | Confirmed cases per 100,000 population. | EEA | Europe |
| Human cases of Lyme disease | Not applicable | Human cases of Lyme disease per 100,000 population. | CDC | USA |
| [Cases of] Lyme disease | Confirmed cases per 100,000 population. | EEA | Europe | |
| Human cases of Lyme disease | Human cases of Lyme disease. | CDC, US EPA | USA | |
| [Cases of] Lyme disease | Rate of confirmed Lyme cases nationwide. Diagnosed by health care providers. | US EPA | USA | |
| Human cases of West Nile Virus Disease | Not applicable | Human cases of West Nile Virus Disease, per 100,000 population. | CDC | USA |
| Human cases of West Nile virus | Human cases of West Nile virus. | CDC, US EPA | USA | |
| West Nile Virus Infection | Confirmed cases per 100,000 population. | EEA | Europe | |
| Cases of neuroinvasive West Nile virus disease | Not applicable | Rate of reported neuroinvasive West Nile virus disease cases across the United States. Neuroinvasive cases, which occur for less than 1 percent of people infected with West Nile virus, are those that affect the brain or cause neurologic dysfunction. | US EPA | USA |
| Human cases of hantavirus cardiopulmonary syndrome (HCPS) | Not applicable | Human cases of hantavirus cardiopulmonary syndrome (HCPS). | CDC, US EPA | USA |
| Malnutrition and food-borne diseases | ||||
| [Cases of] Campylobacteriosis | Not applicable | Confirmed cases per 100,000 population. | EEA | Europe |
| Vibriosis infection | Not applicable | Confirmed cases per 100,000 population. | EEA | Europe |
| Percentage of populationundernourished (urban/rural;women/men) | Not applicable | A measure of food security. The percentageof population undernourishedprovides information on thenumber of people within a population whose dietary energy intake lies below their minimum requirements. | SIDA | Global |
| Prevalence of stunting in children younger than 5 years | Not applicable | Prevalence of stunting in children younger than 5 years (i.e., percentage of children who fell below -2 SD from the length-for-age or height-for-age WHO Child Growth Standards median), data for whom are most readily available, or younger than 2 years, which is the group most sensitive to the interventions. | WHO | Global |
| [Cases of] Salmonellosis | Not applicable | Confirmed cases per 100,000 population. | EEA | Europe |
| [Cases of] STEC/VTEC (toxin-producing Escherichia coli) | Not applicable | Confirmed cases per 100,000 population. | EEA | Europe |
| Human shellfish poisonings | Not applicable | Human shellfish poisonings due to harmful algae blooms. | CDC, US EPA | USA |
| Mental and psychosocial health | ||||
| Mental health | Not applicable | Association between mean annual maximum temperatures and suicide rates. | Lancet, UN | Western Pacific |
Figure 3.

Frequency of severity measures.
Dark boxes represent indicators that measure mortality; light boxes represent indicators that measure injury or illness; medium boxes at the end represent indicators that measure both mortality and morbidity.
3.3. Secondary categorization
From the seven primary categories with indicators reported above, 23 secondary categories were identified (Figure 4). The 73 unique indicators were each classified into the single most relevant secondary category and mapped to illustrate the variation in use of indicators between the different areas of climate change. The most prevalent secondary category indicators were mortality from extreme weather events and illness from zoonoses/vector-borne diseases with 10 and 9 unique indicators respectively. No indicators were identified for the following five secondary categories: illness from mental and psychological health, cold-related illness, mortality from food-borne disease, mortality from malnutrition and mortality from water-borne diseases.
4. Discussion
The main purpose of this scoping review was to map the currently available indicators relevant to human health outcomes that are directly influenced by climate change, to support the development of a transparent, globally generalizable framework and technical platform for official statistics on climate change and health. The scoping review was rigorously carried out and designed in close collaboration with end users; it was conducted according to a registered protocol and with the support of an experienced information specialist.
This review included 20 diverse sources that were, in most cases, syntheses of previous indicator sets and/or incorporated expert opinion. These data were sourced from seven North American, six global (including low- and middle- income countries), four European, two Western Pacific, and one Middle Eastern datasets. Therefore, the overview presented here is comprehensive. We have accounted for duplication and heterogeneity in the included indicators by identifying unique indicators and grouping them with repeated ones, along with multiple definitions (see Table 4). This review makes an important contribution to the work of establishing standardized indicators across countries, which will enable vital work such as analyzing patterns of change over time and supporting the application of methods for the detection and attribution of climate change impacts. 35
The main categories of indicators retrieved were: temperature-related illness and mortality; extreme weather event-related injury and mortality; and air quality-related illness and mortality. There is increasing strength of scientific attribution of the increased intensity, frequency and duration of heatwaves and other extreme weather events, and changes in air quality, to climate change.36,37 Therefore, as climate change intensifies, we can expect more health impacts in these three categories, and consequently the range of available indicators will be useful for tracking the changing burden of disease and associated policy needs.
Five secondary categories did not have climate-sensitive health indicators and understanding this gap is helpful to inform respective official statistics. These indicator gaps were for cold-related illness, mortality from food-borne diseases, mortality from malnutrition, mortality from water-borne disease and illness from mental and psychosocial health. It is interesting to speculate why these secondary categories might have indicator gaps: i) there is limited evidence of attribution from climate change to human health effects, ii) operationalising the concept is challenging and iii) data availability barriers. For instance, focusing on psychosocial health it is surprising there is an absence of indicator as climate change is projected to be the greatest mental health threat of the twenty-first century. 38 Yet, mental health impacts of climate change are under-researched compared with other health areas. 38 Further, while diagnostic codes (e.g., ICD10 codes) capture some aspects of mental health, there is limited globally standardised data on sub-clinical mental wellbeing as it is less readily observable.
We encountered the following challenges with this review:
The review was designed to include indicators related to the direct impacts of climate change on human health. In practice, there were sometimes challenges determining whether an indicator measured direct vs indirect impacts of climate change; for example, the indicator of “pollen days” versus “increase in allergy symptoms” track the same process by which climate change increases the pollen generated by trees, thereby increasing symptoms for those allergic to pollen, but measure different points in the process.
We found that the authors of included sources differed in their decisions about attributing specific indicators to climate change, or classifying impacts of certain climate change-related events, such as wildfires, as being health-related.
4.1. Limitations
Limitations of this scoping review include the following;
The decision to restrict inclusion to global authorities was made on grounds of feasibility. Due to the fact that the included sources were largely syntheses and/or compilations of expert opinion, the potential limitation of this decision was offset by the comprehensiveness of the included sources.
The majority of the included sources came from high-income settings (see Table 3. Characteristics of included studies). This reflects what is available, but highlights the fundamental need for more health research focused on low- and middle-income countries. 39
The determination as to whether an indicator was unique was limited by reported details and entailed subjective assessments by the review team.
4.2. Future work
This scoping review synthesized one category of indicators: direct climate change impacts on population health. It would be valuable to amplify this work with future syntheses of indicators of health-system impacts; indirect human health impacts; vulnerability, exposure and risk; adaptation processes; health-system resilience; institutional engagement; and learning and knowledge management.4,39 Analyzing indirect and/or qualitative indicators could be particularly useful for mental health topics. It would also be valuable to include indicators from outside the health system, relevant to the provision of core health. 4 As well, the indicators we retrieved were designed mainly with data at the national and large regional level; further assessment would be useful to establish the extent to which these indicators are relevant at local or smaller regional levels at various reporting cadences. 10 The additional burden of national reporting of official statistics data to global authorities such as the UN and WHO is minimal in most cases, given that the great majority of the data required is already collected by national governments for their own use while governments which are unable to collect such data for their own statistics are unlikely to do so for international purposes. Future work could delve more deeply into reporting burden, such as consideration of the cadence of reporting, data collection costs and analytical complexity. Lastly, further work to investigate the degree to which the indicators collated here are being used in practice by national statistics organizations would be valuable.
The purpose of this paper is to provide a comprehensive and reproducible shortlist of candidate indicators. The larger project of which this scoping review forms a part involves a wide international collaboration to develop these indicators, including partnering policy makers and statisticians from the UK, Rwanda and Ghana to discuss feasibility. Our approach is to identify the currently most valuable measurement approaches and make these available in a form that can be used by official statistics organisations, not inventing new indicators unless absolutely necessary to meet identified needs. The problems of statistical capacity and limited data availability in LMICs are central considerations, and future work would be beneficial to dive into on-the-ground feasibility across different contexts.
For the task of creating official statistics frameworks, the findings of this scoping review, and future syntheses addressing the gaps listed above, should be amplified with an expert consensus process such as the Delphi method in order to draw on the nuances and networks that subject-matter experts can provide.40,43
5. Conclusion
The goal of policymakers, as climate change intensifies, must be to protect human health and health systems from a range of impacts. To this end, relevant and efficient indicators can track progress and highlight where and when corrections are needed for future planning and to increase the effectiveness of adaptation-related policy-making. 4 Indicators are only as useful as the data available to support them; in countries for which extensive data is available to support analyses by age, gender, socio-economic status and other demographic criteria, decision-making can be more nuanced, which has equity implications given that less-affluent countries often have less-detailed data available.
Our findings make an important contribution to supporting global climate-health policymaking by presenting a comprehensive and up-to-date overview of indicators relevant to the health impacts of climate change. The collection and synthesis of measures of climate-sensitive health outcomes undertaken in this review will aid in provision of a framework and platform for future monitoring of, and adaptation to, the health impacts of climate change-related events. Official statistics can contribute to the measurement and monitoring of various aspects of climate change and support bringing together current and future statistical work into a cohesive framework. Indicators, with their potential to reveal relative positions or show positive or negative change, are crucial for setting targets and monitoring achievement. The list of indicators presented here will have value for official statistics and long-term policy and planning purposes.
Official statistics are produced by governmental organisations and (in most countries) are independent of immediate political control, giving them authority and credibility. Presently there is a lack of harmonized approaches across countries’ official statistics in regard to climate change and health. Addressing this gap, and supporting the required actions with the needed funding, will help to support national monitoring and evidence-based policy-making, always recognizing that policymaking processes are influenced by many factors beyond data availability. 41 The frontiers of climate change science are continually moving. Over time, to help governments meet the urgent imperatives of effective climate action, official statistics offices may come to incorporate new data sources such as satellite observation or processed data published by academic institutions or non-governmental organizations. The incorporation of ‘non-official’ data sources presents a dilemma which many governmental organisations are already grappling with, and it requires finding a principled balance between data quality and known provenance on the one hand, and increasing pressures for timeliness and granularity on the other. The ability of official statistics offices, especially in low- and middle-income countries, to monitor the effects of climate change will be increased by the provision of practical, coherent standards and open-source tools. Both producers and consumers of climate change research will benefit from faster study development based on shared approaches and a more consistent “language” for communication of findings. Ultimately these benefits will translate into a better-informed international community and more effective, evidence-based climate change interventions. 42
Acknowledgements
The authors would like to thank Mr D Salzwedel, MLIS, for development and execution of the search strategy. In addition, Drs. L Grant, K Konnyu and N Skoetz reviewed and provided valuable feedback on the protocol. This publication has been produced by the Cochrane Planetary Health Thematic Group as part of the Standards for Official Statistics on Climate-Health Interactions (SOSCHI) project, led by the UK Office for National Statistics and funded by Wellcome.
ORCID iDs: Denise Thomson https://orcid.org/0000-0002-4972-5331
Meghan Sebastianski https://orcid.org/0000-0002-5206-8731
Megan Nuspl https://orcid.org/0000-0002-3137-9928
Vijendra Ingole https://orcid.org/0000-0002-3205-7218
Myer Glickman https://orcid.org/0000-0001-6067-3811
Funding: This research was funded in whole or in part by the Wellcome Trust (Grant number: 224682/Z/21/Z). For the purpose of open access, the author has applied a CC-BY public copyright license to any author accepted manuscript version arising from this submission.
The author(s) declared no potential conflicts of interest with respect to the research, authorship, and/or publication of this article.
References
- 1.Radermacher WJ. Official statistics 4.0: Verified facts for people in the 21st century. Switzerland: Springer Cham, 2021. [Google Scholar]
- 2.Van Halderen G, Cho B. Climate change and implications for statistics. Stat J IAOS 2009; 26: 41–46. [Google Scholar]
- 3.Cissé G, McLeman R, Adams H, , et al. 2022: Health, wellbeing, and the changing structure of communities. In: Pörtner HO, Roberts DC, Tignor M, Poloczanska ES, Mintenbeck K, Alegría A, et al., (eds). Climate change 2022: impacts, adaptation and vulnerability contribution of working group II to the sixth assessment report of the intergovernmental panel on climate change. Cambridge, UK and New York, NY, USA: Cambridge University Press; 2022. p. 1041–1170. [Google Scholar]
- 4.Ebi KL, Boyer C, Bowen KJ, et al. Monitoring and evaluation indicators for climate change-related health impacts, risks, adaptation, and resilience. Int J Environ Res Public Health 2018; 15. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 5.Bell E. Readying health services for climate change: A policy framework for regional development. Am J Public Health 2011; 101: 804–813. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 6.Haines A, Ebi K. The imperative for climate action to protect health. N Engl J Med 2019; 380: 263–273. [DOI] [PubMed] [Google Scholar]
- 7.Bolitho A, Miller F. Heat as emergency, heat as chronic stress: Policy and institutional responses to vulnerability to extreme heat. Local Environ 2017; 22: 682–698. [Google Scholar]
- 8.Death Review Panel. Extreme heat and human mortality: A review of heat-related deaths in B.C. in summer 2021. Victoria, B.C.: Chief Coroner of British Columbia, 2022. [Google Scholar]
- 9.Smith N, Donaldson M, Mitton C. Communication in disasters to support families with children with medical complexity and special healthcare needs: A rapid scoping review [Internet]. British Columbia (Canada): SPOR Evidence Alliance; 2021. [cited 2024 Jan 31]. Available from: https://sporevidencealliance.ca/wp-content/uploads/2022/05/SPOREA_Communication-in-disasters-CMC-rapid-scoping-review_FinalReport.pdf
- 10.Ebi KL, Ogden NH, Semenza JCet al. et al. Detecting and attributing health burdens to climate change. Environ Health Perspect 2017; 125: 085004. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 11.Glickman M, Green M. Standards for official statistics on climate-health interactions. Presented at: Office for National Statistics Wellcome Project Meeting. Office for National Statistics; PRESENTATION DATE. 2022-FEB-21; UK.
- 12.Arksey H, O'Malley L. Scoping studies: towards a methodological framework. Int J Soc Res Methodol 2005; 8: 19–32. [Google Scholar]
- 13.Tricco AC, Lillie E, Zarin W, et al. PRISMA Extension for scoping reviews (PRISMA-ScR): checklist and explanation. Ann Intern Med 2018; 169: 467–473. [DOI] [PubMed] [Google Scholar]
- 14.World Health Organization. Climate change 2023 [Internet]. Geneva (Switzerland): World Health Organization;2023 [updated 2023; cited 2024 Jan 31]. Available from: https://www.who.int/news-room/fact-sheets/detail/climate-change-and-health
- 15.Berko J, Ingram DD, Saha Set al. et al. Deaths attributed to heat, cold, and other weather events in the United States, 2006–2010. Natl Health Stat Report 2014; 76: 1–15. [PubMed] [Google Scholar]
- 16.Bernard SM, Samet JM, Grambsch A, et al. The potential impacts of climate variability and change on air pollution-related health effects in the United States. Environ Health Perspect 2001; 109: 199–209. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 17.Centres for Disease Control Climate Health Program. Heat and health tracker [Internet]. Atlanta (USA): Centres for Disease Control; 2018. [updated 2023; cited 2024 Jan 31]. Available from: https://ephtracking.cdc.gov/Applications/heatTracker/
- 18.Council of State Territorial Epidemiologists. Environmental health indicators: Climate change [Internet]. Atlanta (USA): Council of State Territorial Epidemiologists; 2018. [updated 2018; cited 2024 Jan 31]. Available from: https://www.cste.org/page/ehindicatorsclimate
- 19.Dora C, Haines A, Balbus J, et al. Indicators linking health and sustainability in the post-2015 development agenda. Lancet 2015; 385: 380–391. [DOI] [PubMed] [Google Scholar]
- 20.English PB, Sinclair AH, Ross Z, et al. Environmental health indicators of climate change for the United States: findings from the State Environmental Health Indicator Collaborative. Environ Health Perspect 2009; 117: 1673–1681. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 21.European Climate Adaptation Platform Climate-ADAPT. Indicators on climate change and health [Internet]. Copenhagen: (Denmark: ): European Commission & European Environment Agency; 2022. [cited 2024 Jan 31]. Available from: https://climate-adapt.eea.europa.eu/en/observatory/evidence/indicators_intro [Google Scholar]
- 22.European Environment Agency. Indicators [Internet]. Copenhagen, Denmark: European Environment Agency; 2016. [cited 2024 Jan 31]. Available from: https://www.eea.europa.eu/en/analysis/indicators
- 23.European Environment Agency. Climate change as a threat to health and well-being in Europe: focus on heat and infectious diseases. Luxembourg: Publications Office of the European Union; 2022. Report No.: 7/2022. [Google Scholar]
- 24.Jung EM, Jagals P, Brereton C, et al. Children’s environmental health indicators in context of the sustainable development goals for small island developing states. Int J Environ Res Public Health 2018; 15: 1404. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 25.Lay CR, Mills D, Belova A, et al. Emergency department visits and ambient temperature: Evaluating the connection and projecting future outcomes. GeoHealth 2018; 2: 182–194. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 26.Romanello M, Di Napoli C, Drummond P, et al. The 2022 report of the Lancet Countdown on health and climate change: Health at the mercy of fossil fuels. Lancet 2022; 400: 1619–1654. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 27.Swedish International Development Agency. Environmental and Climate Change Indicators: Guidance at country and sector level. Stockholm, Sweden; 2011. Report No.: SIDA61411en.
- 28.United Nations Economic and Social Commission for Western Asia. Climate change-related statistics in the Arab region: A proposed set of indicators. Beirut, Lebanon; 2017. Report No.: E/ESCWA/SD/2017/3.
- 29.United States Environmental Protection Agency. Climate change indicators in the United States, 2016. Fourth edition. Washington, USA; 2016. Report No.: EPA 430-R-16-004.
- 30.van Daalen KR, Romanello M, Rocklov J, et al. The 2022 Europe report of the Lancet Countdown on health and climate change: Towards a climate resilient future. The Lancet Public Health 2022; 7: e942–ee65. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 31.World Health Organization. Global reference list of 100 core health indicators (plus health-related SDGs). Geneva, Switzerland, 2018, Report No.: WHO/HIS/IER/GPM/2018.1.
- 32.World Health Organization. WHO global strategy on health, environment and climate change: The transformation needed to improve lives and wellbeing sustainably through healthy environments. Geneva, Switzerland; 2020. ISBN: 978 92 4 000037 7
- 33.World Meteorological Organization. Atlas of mortality and economic losses from weather, climate and water extremes (1970–2019). Geneva, Switzerland, 2021, Report No.: WMO-No. 1267.
- 34.Zhang Y, Beggs PJ, Bambrick H, et al. The MJA-Lancet Countdown on health and climate change: Australian policy inaction threatens lives. Med J Aust 2018; 209: 474. [DOI] [PubMed] [Google Scholar]
- 35.Males J, Carlson CJ, Alam MS, et al. The health burden of climate change: A call for global scientific action. PLOS Climate 2023; 2. [Google Scholar]
- 36.Clarke B, Otto F, Stuart-Smith Ret al. et al. Extreme weather impacts of climate change: an attribution perspective. Environ Res: Climate 2022; 1. [Google Scholar]
- 37.World Weather Attribution. Climate change fueled extreme weather in 2023; expect more records in 2024 [Internet]. London: (UK: ): World Weather Attribution; 2023. [cited 2024 Jan 31]. Available from: https://www.worldweatherattribution.org/climate-change-fuelled-extreme-weather-in-2023-expect-more-records-in-2024/. [Google Scholar]
- 38.Charlson F, Ali S, Augustinavicius J, et al. Global priorities for climate change and mental health research. Environ Int 2022; 158: 106984. [DOI] [PubMed] [Google Scholar]
- 39.Adam T, Ralaidovy AH, Ross AL, et al. Tracking global resources and capacity for health research: time to reassess strategies and investment decisions. Health Res Policy Syst 2023; 21: 93. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 40.Thomson D, Varangu L, Webster RJ. A climate resilience maturity matrix for Canadian health systems. Healthc Manage Forum 2023; 36: 217–223. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 41.Cairney P. The Politics of evidence-based policy making. London, UK: Palgrave Macmillan/Springer Nature, 2016. [Google Scholar]
- 42.Office for National Statistics. Standards for official statistics on climate-health interactions [Internet]. London: (UK: ): Office for National Statistics; 2024 [cited 2024 Dec 5]. Available from: https://www.ons.gov.uk/aboutus/whatwedo/programmesandprojects/standardsforofficialstatisticsonclimatehealthinteractions [Google Scholar]
- 43.Taylor E. We agree, don't we? The delphi method for health environments research. HERD 2020; 13: 11–23. [DOI] [PubMed] [Google Scholar]
