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SOSCHI Framework Overview

The SOSCHI framework covers a wide range of health-related topics which are affected by climate change, namely waterborne diseases, vector-borne diseases, temperature-related health effects, mental health, health effects of extreme weather events (wildfire and floods), health effects of air pollution and air-borne diseases, undernutrition and food-borne diseases, and healthcare systems and facilities. The final SOSCHI Framework report and final topic documents for selected topic documents are available, for all other topics alpha versions are available (see section on "Guidance and tools to support user implementation").

Climate-Health Impact Pathways
Diagram showing overview of SOSCHI framework
Framework development process

The SOSCHI framework has been developed by ONS in collaboration with partners from the African Institute for Mathematical Studies (AIMS) in Rwanda, and the Regional Institute for Population Studies (RIPS) in Ghana and with input from the UK Health Security Agency, the Cochrane Planetary Health Theme Group, and a large number of leading subject experts.

See the About us page for more information.

Figure 1 illustrates the timeline and stages of the SOSCHI project. The activities that defined the earlier stages of the project are described in detail in the previously published Discovery Phase Report and Alpha phase report.

Discovery Phase (2022 - 2023)

ONS Climate and Health team begin

  • Project scoped
  • Partner selection and onboarding

Alpha Phase (2023 - 2024)

First draft of statistical framework and platform

  • Topic expert group established
  • Internal testing with project partners

Beta Phase (2024 - 2025)

Further refinement of framework and platform

  • Selected indicator calculators online
  • Testing with beyond partner countries
  • Feedback from experts and global users

Launch (2026)

Final drafts signed off

  • Work with UN and key stakeholders
  • Launch platform and publish framework

The involvement of experts and users throughout the development process has ensured that proposed indicators are based on state-of-the-art statistical methods and can be implemented beyond the project partner countries.

The “topic pages” also include information on the specific experts engaged in the development of the SOSCHI framework.

Guidance and tools to support user implementation

If you want to produce any of the priority indicator metrics included in the SOSCHI framework, you will first need to identify and prepare the input data sources. Once the input data is in the required structure, you can either use the Climate-Health R Package or the indicator tool for selected topics, to produce selected climate-health indicator metrics for your country or area.

Additional guidance is available to support users (e.g. topic documents, guidance videos etc). The available guidance and tools available for each topic in the SOSCHI framework are summarised in the table below.

The guidance tools include:

  • Topic introduction: state of knowledge on the topic and rationale of topic and indicator selection
  • Methods documents: outline of statistical approaches to measure the headline indicator
  • Metadata sheets: summary of the headline indicator metrics and their component parts to support user implementation
  • R code: Published Climate-Health R Package (available via the SOSCHI GitHub repository or CRAN in RStudio), for users to run in their offline workflow and adapt the methods for measuring climate-health indicator metrics for their local context using their own data
  • Online tool: Ready to use analysis tool for measuring climate-health indicator metrics are in development, and will be available on this platform, based on the generic model using their own data upload, no prior knowledge of R coding required
Important information:

The SOSCHI framework topics are at a different stage of readiness. The first six selected topics in the table below have been prioritised, with more comprehensive guidance to support users in implementing these to produce indicator metrics based on the input data sources from their country.

Key

  • Included
  • In progress
  • Not included
Framework topics Alpha Version Final Version R Package Indicator Tool
Waterborne diseases (diarrhea) Included Included Included In progress
Waterborne diseases (chemical contaminants) In progress Not Included Not Included Not Included
Vector-borne diseases (malaria) Included Included Included In progress
Temperature-related health effects Included Included Included In progress
Mental health (suicide) Included Included Included In progress
Health effects of air pollution Included Included Included Not Included
Airborne diseases (cerebrospinal meningitis) Included Not Included Not Included Not Included
Health effects of extreme weather events (wildfires) Included Included Included In progress
Health effects of extreme weather events (flooding) Included Not Included Not Included Not Included
Undernutrition and food-borne diseases Included Not Included Not Included Not Included
Healthcare systems and facilities Included Not Included Not Included Not Included
Partner country implementation of the framework

The aim of the SOSCHI Framework is to support National Statistics Offices (NSOs) in systematic monitoring of climate change outcomes and help to build relevant expert capacity globally, especially in low- and middle-income countries' (LMIC) statistical institutions.

The work has been developed collaboratively between partners in Ghana, Rwanda and the UK so that experience and priorities in Africa, where some of the worst climate change impacts are already evident, are central to the development. For each of these partner countries, implementation plans are in progress, to share experiences and lessons learned to inform global implementation.

UN endorsement of the SOSCHI framework

The main benefit of the SOSCHI framework, and its contribution to this field, is providing National Statistics Organisations (NSOs) and other government institutions with harmonised indicators, validated methods and practical tools, to improve the monitoring of climate change impacts on health.

The following six headline indicators from the SOSCHI framework were endorsed by the 57th session of the United Nations Statistical Commission (3-6 March 2026) as part of the authoritative UN Global Set of Climate Change Statistics and Indicators.

Important information:
  • 44.1 Incidence of diarrheal disease cases attributable to (a) heat and (b) rainfall
  • 44.2 Incidence of malaria cases attributable to (a) heat and (b) rainfall
  • 45.1 Mortality from all causes attributable to (a) heat and (b) cold
  • 45.2 Mortality from suicide attributable to excess heat (proxy for mental health)
  • 46.1 Mortality attributable to short-term effects of Ambient air quality (PM2.5)
  • 46.2 Mortality attributable to effects of wildfire smoke (PM2.5)

The proposal was developed with the support of the UN Expert Group on Environment and Climate Change Statistics (EG-ECCS) and its Sub-Group on Climate and Health, and updates the metadata of Global Set indicators 44, 45 and 46 in line with the definitions and methodologies developed by the project.

Diagram showing overview of SOSCHI
framework

See the about us page for more information on those countries and institutions involved in the EG-ECCS climate-health sub-group, and the "events page" for information on our global engagement. For more information on our global stakeholder engagement, see the SOSCHI framework report (section 2.3: Relationship to other frameworks).

Temperature-related health effects

Climate change is altering global temperature trends. Increasing the frequency, intensity, and duration of temperature extremes in many countries. Rising global temperatures, and the impact on health are of global concern. Current research suggests that globally there are more cold-related deaths than heat-related. However, the global rate of increased climate-related mortality from heat is predicted to offset the rate of decrease in mortality from cold during the 21st Century.

Important information:

This topic explores the relationship between temperature as a climate hazard and the impacts on human health.

UN endorsement:
UN endorsement

The methods for measuring the headline outcome indicator for this topic were endorsed by the 57th United Nations Statistical Commission to include in the Global Set of Climate Change Statistics and Indicators (see decision 57/109 (b) in the Final Report ). This will be included in the Global Set metadata as:

  • Indicator 45: Incidence of heat and cold related illnesses or excess mortality:
    45.1 Mortality from all causes attributable to (a) heat and (b) cold
Impact Pathway
Diagram showing pathways between climate
change and temperature-related health impacts. At the top left, climate drivers and hazards include increased frequency
and intensity of extreme temperatures which lead to heatwaves and cold spells. At the top right, exposure and
vulnerability include direct or repeated climate hazard exposure and socio-economic factors such as age, gender,
occupation and pre-existing health conditions. These factors interact and flow downward toward physiological impacts and
health outcomes. Physiological impacts include heat dissipating mechanisms being negatively impacted due to heat, and
heat retaining mechanisms negatively impacted due to cold. Health outcomes are caused or exacerbated by high and low
temperatures, and mortality risk increases are temperatures become more extreme. Adaptation and mitigation measures—such
as temperature-related warning systems to support health and social care systems, or nature-based solutions such as
urban forests and green infrastructure to facilitate cooling—are shown intervening to reduce negative impacts.
Headline Indicator
Important information:

The priority indicator developed for this topic is all-cause mortality attributable to high and low temperatures.

There are two main aims of this indicator:

  • to allow users to estimate the relationship between temperature and mortality using historical data records
  • to allow users to produce modelled estimates of the impact of high and low temperatures on mortality

Further justification for the focus on this indicator is explained in the Topic introduction , which also outlines supplementary and additional indicators that are not in scope for the current SOSCHI framework but are recommended for future development.

The indicator has four component parts:

Important information:

Relative risk for the temperature-mortality association

Important information:

Attributable number as the number of deaths attributable to high and low temperatures

Important information:

Attributable fraction as the percentage of deaths attributable to high and low temperatures

Important information:

Attributable rate as the number of deaths per 100,000 population attributable to high and low temperatures

For guidance on the process for calculating these indicator metrics, see the Methodology section below.

Sub-indicator
Important information:

This methodology also covers the following sub-indicator which specifies the underlying cause of death: Non-communicable disease (NCD) mortality attributable to high and low temperatures and produces the same outputs as the headline indicator noted above.

The interaction between climate change and health is especially evident in the growing burden of NCDs, which are further exacerbated by environmental shifts.

Table 1 of the methodology document specifies codes for underlying cause of death related to NCDs as captured in the SOSCHI NCD Topic Introduction document. These codes refer to the WHO International Classification of Diseases, 10th edition (ICD-10) or 11th edition (ICD-11) . These codes represent the underlying cause of death, which in many countries is the only health condition reported from death registration.

NCDs was previously a separate topic in the SOSCHI framework.

Topic Introduction (opens in a new window)
Policy Relevance

This indicator can give insights into how high and low temperature days may be impacting physical health and how this may vary geographically and impact vulnerable groups in society.

This indicator can therefore:

  • inform national adaptation plans (NAPs) and targeted resilience strategies
  • guide climate and public health policy to help mitigate risks and improve health outcomes
Methodology

The indicator quantifies the short-term impacts of high and low temperatures on mortality using a quasi-Poisson time series regression with a distributed lag non-linear model (DLNM). This model accounts for both the delayed health effects seen after the occurrence of a high or low temperature day, and the non-linear relationship between temperature and mortality i.e. mortality risk increases as temperatures become more extreme.

The model estimates the temperature–mortality relationship, relative to the lowest risk temperature i.e. the minimum mortality temperature. When multiple geographies are analysed, the results are combined using a multivariate meta-analysis to strengthen estimates and produce results for the combined geographical area e.g. national level.

Important information:
Understand the method

Read the Mortality attributable to high and low temperatures: methodology for details on the modelling approach, the data needed, and guidance on interpreting results.

Important information:
Develop bespoke analysis

For flexible, reproducible analysis or to adapt methods to your country or region, use the R package , which provides program code for the priority indicators.

Important information:
Online tools for indicator analysis

Tools for selected indicators are in development. These will allow users to run quick baseline estimates and simple charts without writing code; it supports secure temporary uploads and downloadable outputs.

Data Requirements and Guidance

This indicator requires:

  • daily mortality data from national administrative records
  • population estimates from national statistical agencies
  • daily mean temperature and other optional climatic variables from government meteorological offices

Where data points are missing, proxy datasets may be used as recommended in section 2.2 of Mortality attributable to high and low temperatures: methodology . Guidance on required variables and how to prepare the dataset can also be found in section 2.3 and 3.2.

FAQs

How is the temperature-related health effects topic relevant?

Climate change is leading to more frequent and extreme hazards that have direct and indirect effects on populations. For example, increasingly high and low temperatures have been found to show an impact on mortality risk.

What insights can this indicator provide?

The estimated change of mortality risk due to high or low outdoor temperatures, compared to the lowest risk temperature for the area. It also estimates the number, rate and proportion of deaths attributable to high or low temperatures, i.e. the number, rate or proportion of deaths that have occurred due to high or low temperatures.

The results can help identify which groups are most vulnerable at certain high or low temperatures. This can help plan interventions to build resilience to mitigate the risks associated with the changing temperature patterns.

See the methodology document for details on the indicator metrics.

Who can run this indicator analysis?

This indicator can be used by analysts who meet the following criteria:

  • have access to daily mortality data and daily temperature data
  • have access to population estimates for the applicable geography/geographies or other disaggregated groups
  • have some understanding of how to interpret the indicator metrics, and can communicate uncertainty using statistical power, using guidance provided in section 4 of the methodology document
How can I run the indicator analysis?

Users can apply the methodology to their own daily temperature and mortality data to run a time series model with our open-source R package available on GitHub or CRAN.

Please see the Analysis pathways guidance page for more detail.

Can I use weekly or monthly data?

Daily data provide the highest level of accuracy for this indicator. However, previously published literature (see methodology document section 1 for more info and references) has demonstrated that the method produces reasonable estimates with weekly data in the context of Europe.

See section 2.2 of the methodology document for alternative data sources that can be used as proxy data.

The method is not applicable to monthly data.

What geographical level can I run the analysis for?

The methodology can be applied to any geographical level e.g. national, local, but the power of the data must be considered. The R package includes a function to produce this. Users should aim for 80% power and document whether this has been achieved when communicating results (See section 3.7 and 4 of Mortality attributable to high and low temperatures: methodology ).

Can I disaggregate by different demographics?

Yes, the data will need to be subset prior to running the analysis e.g. including death count columns for each age group. Users should consider whether their data has enough power to help achieve more accurate results. The R package includes a function to produce this. Users should aim for 80% power and document whether this has been achieved when communicating results (See section 3.7 and 4 of Mortality attributable to high and low temperatures: methodology ).

Why are the temperature percentile thresholds for high and low temperatures set at the 97.5th and 2.5th percentiles, respectively?

These were set based on existing literature (see methodology document section 3.1 for more info and references) and consultation with a group of climate and health international experts. These are based on the temperature distribution over the whole time series provided for each geographical area. These are the default settings, and we encourage users to apply these for consistent official reporting. However, users can adjust these if other percentiles are more relevant for their context.

If global temperatures show an increasing trend, why does the indicator investigate cold temperatures too?

Anthropogenic climate changes have affected weather and climate extremes in every region of the globe. These are predicted to have impacts on both warming and cooling under future climate change scenarios. Published estimates report approximately 489,075 heat-related deaths globally, between 2000-2019. However, a higher number of deaths have been estimated related to exposure to cold temperatures, with estimations reaching approximately 4,594,098 cold-related deaths globally, during the same period. However, the global rate of increased climate-related mortality from heat is predicted to offset the rate of decrease in mortality from cold during the 21st Century. This will lead to net mortality from high and low temperatures increasing.

How do I interpret the indicator analysis results?

See section 4: communication and interpretation of the methodology document for guidance on interpreting the indicator metrics outlined above.

Also see sections 2.5 and 5 of the methodology document respectively to understand the data and methodology limitations of the indicator.

Are these direct counts of deaths caused by high and low temperatures?

No, these are estimates based on a statistical model and not observational. These are produced by modelling the association between daily mortality counts and daily mean temperature. This association is then used to estimate the attribution to high and low temperatures. As these are modelled estimates there are uncertainty around the statistics that should be considered in any interpretation of results.

For broader questions that apply across the platform, please see our General FAQs section.

Related Topics

Topic Expert Group

The Topic Expert Groups (TEG) were set up to review climate and health topics and guide what we measure and how we measure it. The groups bring together internal and external specialists who advise on indicators and methods, share subject knowledge, and help quality assure draft outputs before publication.

  • Dr. Aaron Bernstein

    Centers for Disease Control and Prevention

  • Adam Gardiner

    UK Climate Change Committee (previously)

  • Dr. Ana Bonell

    London School of Hygiene & Tropical Medicine

  • Sir Andrew Haines

    London School of Hygiene & Tropical Medicine

  • Dr. Anna Freni Sterrantino

    The Alan Turing Institute

  • Dr. Anna Rom

    UK Health Security Agency

  • Prof. Antonio Gasparrini

    London School of Hygiene & Tropical Medicine

  • Dr. Charles Simpson

    University College London

  • Dr. Christophe Sarran

    UK Met Office

  • Dr. Clare Heaviside

    University College London

  • Denise Thomson

    Cochrane Thematic Group

  • Dr. Emil Ivanov

    United Nations Statistics Division

  • Dr. Erik Svendsen

    Centers for Disease Control and Prevention

  • Dr. Frederike Garbe

    Public Health Scotland

  • Gemma Holmes

    UK Climate Change Committee

  • Dr. Helen Macintyre

    UK Health Security Agency

  • Ian Dwyer

    UK Office for National Statistics

  • Isabella Tortora-Brayda di Belvedere

    Public Health Scotland

  • Prof. Kristie Ebi

    University of Washington

  • Prof. Majid Ezzati

    Imperial College London

  • Marina Walawender

    Lancet Countdown

  • Prof. Michael Davies

    UK Climate Change Committee

  • Mo Davies

    UK Health Security Agency

  • Paul Schramm

    Centers for Disease Control and Prevention

  • Richard Millar

    UK Climate Change Committee

  • Dr. Ricky Nathvani

    Imperial College London

  • Dr. Ross Thompson

    UK Health Security Agency

  • Prof. Shakoor Hajat

    London School of Hygiene & Tropical Medicine

  • Dr. Shubhayu Saha

    Centers for Disease Control and Prevention (previously)

Important information:

The framework topic documents are a final version produced as part of the SOSCHI project (Wellcome grant no. 224682/Z/21/Z). Please note that as this is an emerging topic area, indicators and methods are subject to change. Notices will be issued on this page to inform users of any changes to the information captured.

For more information on the selection criteria used for prioritising the SOSCHI topics and the development process, see the SOSCHI Framework Page .

We recommend that the proposed indicators, methods and tools (e.g. R code) described on this page can be used for official statistics reporting. See the SOSCHI Framework Page for information on the endorsement of the proposed indicators.

Last updated: 14/05/2026

Health effects of extreme weather events

Contents

Health effects of wildfire-related PM2.5

Climate change is increasing the frequency, intensity, and duration of hot and dry conditions, raising the risk of wildfires in many regions. Wildfires are uncontrolled or unplanned fires that occur in vegetated areas. Their impacts extend beyond the burned areas, affecting ecosystems, economies and human health. A major health hazard from wildfires is its associated smoke and air pollution. Vulnerability to this exposure is controlled by demographic and socioeconomic factors, thus risk is not distributed evenly within populations.

Important information:

This topic area focuses on measuring population-level exposure to wildfire-related PM2.5 and estimating its short-term impacts on health.

UN endorsement:
UN endorsement

The methods for measuring the headline outcome indicator for this topic were endorsed by the 57th United Nations Statistical Commission to include in the Global Set of Climate Change Statistics and Indicators (see decision 57/109 (b) in the Final Report ). This will be included in the Global Set metadata as:

  • Indicator 46: Climate-induced air pollution:
    46.2 Mortality attributable to effects of wildfire smoke (PM2.5)
Impact Pathway
Diagram showing how climate drivers and hazards
such as frequent, intense hot temperatures increase wildfire risk leading to smoke exposure that affects populations
differently depending on vulnerability. Inhaling wildfire smoke (especially wildfire-related PM2.5) lead to
physiological impacts that can lead to several health outcomes, including increased mortality, respiratory and
cardiovascular risks. Adaptation and mitigation actions can reduce exposure, protect health and limit future wildfire
risk.
Headline Indicators
Important information:

The priority indicator developed within this topic is All-cause mortality attributable to wildfire-related PM2.5.

It was agreed to prioritise this indicator as wildfire-related PM2.5 is strongly linked to adverse health outcomes and has a well-established evidence base in epidemiological studies. Wildfire-related PM2.5 is also consistently measured across regions, enabling comparable and policy relevant assessments of wildfire-related health impacts.

Further justification for focusing on this indicator is provided in the  Topic introduction  . This methodology also covers two additional indicators, with further details available in the methods documentation:

  • respiratory mortality attributable to wildfire-related PM2.5
  • cardiovascular mortality attributable to wildfire-related PM2.5

Each indicator has three component parts:

Important information:

Relative risk of mortality associated with wildfire-related PM2.5

Important information:

Number of deaths attributable to wildfire-smoke PM2.5

Important information:

Deaths per 100,000 population attributable to wildfire-related PM2.5

For guidance on the process for calculating these indicator metrics, see the Methodology section below.

Policy Relevance

This indicator can provide insights into how wildfire PM2.5 exposure is impacting human mortality, and how these risks vary across locations and vulnerable groups. While wildfire-related mortality does not capture the full spectrum of health impacts (e.g., morbidity or long-term exposure effects), it serves as a robust proxy for the most severe acute outcomes associated with wildfire events.

This indicator can therefore:

  • monitor and quantify the health impacts of wildfires, particularly mortality risk
  • identify geographic and population-level disparities, including the most vulnerable groups
  • identify seasonal patterns and monitor wildfire mortality risk over time
  • inform national adaptation plans (NAPs) and climate resilience strategies
  • guide public health, environmental, and emergency response policies to reduce risks and improve outcomes
Methodology

This indicator estimates mortality attributable of wildfire-related PM2.5 by comparing exposure on days when deaths occur with similar nearby days. It accounts for seasonal patterns and long-term trends and examines delayed effects over several days. Results are reported as the relative increase in mortality risk for every 10 µg/m³ rise in wildfire-related PM2.5.

Important information:
Understand the method

Read the all-cause mortality attributable to wildfire smoke: methodology for details on the modelling approach, the data needed, and guidance on interpreting results.

Important information:
Develop bespoke analyses

For flexible, reproducible analysis or to adapt methods to your country or region, use the R package , which provides program code for the priority indicators.

Important information:
Online tools for indicator analysis

Tools for selected indicators are in development. These will allow users to run quick baseline estimates and simple charts without writing code; it supports secure temporary uploads and downloadable outputs.

Data Requirements and Guidance

The following data are needed for this indicator production:

  • daily all-cause mortality from national administrative records.
  • daily mean temperature from governmental meteorological offices.
  • population estimates from national offices
  • daily Wildfire-related PM2.5 from open source dataset.

Where this data is unavailable or observations are incomplete, proxy datasets may be used. Further information on these potential sources as well as required variable names and formats are outlined in section 2 of the All-cause mortality attributable to wildfire smoke: methodology . A minimal example of the data template is provided on the Indicator tool page to help structure uploads before running the calculator.

FAQs

Why was this statistical model used?

The statistical approach used is time stratified case crossover design with conditional quasi-Poisson regression model. This is appropriate for analysing acute health impacts of short-term wildfire related PM2.5 exposure. It allows to compare health outcome on high wildfire PM2.5 exposure days with nearby non wildfire PM2.5 exposure days. This approach controls for season, long-term trends, and day of the week.

The methodology was developed with guidance and consultation from Topic Expert Group and further information can be found in methodology documentation .

What does the wildfire indicator show?

The indicator shows the short-term effects of wildfire related PM2.5 on daily mortality. It quantifies relative risk of death associated with wildfire smoke exposure. It also estimates proportion of deaths attributable to exposure and mortality rates per 100,000, standardised so results are easily comparable across regions. Detailed information can be found in the methodology documentation.

Who should use this indicator tool?

The indicator is intended for users who need to assess the impact of wildfire-related PM2.5 exposure on human mortality. Our target users are global producers of official statistics, academics, students, NGOs and also policymakers who can use the statistics to support and evidence action against climate hazards.

Why was wildfire-related PM2.5 chosen to measure exposure?

Wildfire related PM2.5 is one of the main harmful components of wildfire smoke. PM2.5 refers to very fine particles that when inhaled, can go deep into the lungs and enter the bloodstream, where they can cause wide range of health issues. Studies show that wildfire related- PM2.5 has distinct toxicological characteristics compared to PM2.5 from other ambient air pollution sources and may be more harmful to human health. It is also one of the most well studied wildfire components, with strong evidence linking to health risks. Because wildfire‑related PM2.5 captures both nearby and transported smoke and has a well‑established scientific basis for measuring exposure, it was selected as the primary indicator. For further reading, please refer to methods document.

How are wildfires events detected and measured?

When using this methodology, we recommend users to use this dataset provided by Finnish Meteorological Institute. It uses satellite data (MODIS instrument onboard of Aqua and Terra satellite) combined with atmospheric modelling (SILAM chemical transport model) to estimate the dispersion of fire related PM (particulate matter). The dataset has global coverage, for further information – please refer to the Wildfires methodology documentation .

What health data does the wildfire indicator use?

To run the wildfire analysis, users require daily all-cause mortality data. List of supplementary indicators and related data requirements can be found in the methods document. In all cases, we recommend users to follow data preparation procedures as listed in methods document (section 3.2) prior to analysis.

How often is wildfire data updated?

This version of wildfire methodology uses wildfire-related PM2.5 (fine smoke particles) data developed by the Finnish Meteorological Institute and is updated annually. Please refer to methodology documentation for further details.

Can I use weekly or monthly deaths count data?

Weekly or monthly aggregated death count data are not compatible with this methodology as this approach looks at the short-term health impact and is designed to compare specific exposure days to low exposure days. Also, weekly or monthly aggregations smooths over wildfire smoke days which are typically intense, short-lived and highly variable within a few days.

What time period is required to run wildfire analysis?

There is no single fixed minimum, but in practice you would need a few months of daily data to run the wildfire analysis. For more reliable results, it is advised to use several months to multiple years of data, ideally covering a full wildfire season. Please note that there would be model bias if data consists of only wildfire events and vice versa. For further methodology analysis, please refer to documentation.

How reliable are the estimates that are produced?

Users should carefully follow the recommended data preparation procedures to ensure valid results. We strongly recommend using the GitHub analysis package, which includes built-in model validation steps to help ensure robust estimates are produced. All results should be interpreted as statistical estimates, not actual counts of death, and should always be considered together with their confidence intervals.

The analysis is based on historic data and does not provide real-time estimates. Wildfires vary substantially between regions, and new or emerging wildfire-affected areas may not yet be fully captured in the data. For further information, please refer to methods document.

Can I compare wildfire impacts between regions or years?

Yes, provided data is set up and ready to use as recommended by the methodology document (section 2.3, 3.2 and 3.3), this indicator analysis will provide comparable results.

How should I interpret a negative or zero value?

A value of zero indicates no detectable association between wildfire-related PM2.5 and mortality for the time period. A negative estimate does not imply wildfire smoke is protective but should be interpreted as no evidence of an increased risk. Negative values can arise from limited sample size and/or statistical uncertainty. Estimate results should be considered together with its confidence interval.

How should I interpret the wildfire-health indicator results?

All results from the analysis show statistical associations between wildfire‑related PM2.5 and mortality. They estimate how many deaths are linked to this exposure, not a direct count of observed deaths. For detailed guidance on how to interpret and communicate the indicator results, please refer to methodology documentation (section 4).

How can policymakers use this data to reduce health risk from wildfires?

The analysis results can quantify how real health impacts from wildfire-related PM2.5 has changed over time and can provide the evidence for action. With recommended disaggregation, the data can be used to inform for targeted prevention and preparedness.

For broader questions that apply across the platform, please see our General FAQs section.

Related Topics

Topic Expert Group

The wildfires topic expert group (TEG) was setup to review this topic and guide what we measure and how we measure it. The group brings together internal and external specialists who advise on indicators and methods, share subject knowledge so we build on existing work and good practice, and help quality assure draft outputs before publication.

  • Professor Tarik Benmarhnia

    University of California, San Diego

  • Professor Carlos Gould

    University of California, San Diego

  • Professor Mikhail Sofiev

    Finnish Meteorological Institute

  • Dr Qiao Zhu

    Emory University

  • Professor Yuming Guo

    Monash University

  • Professor Yun Hang

    University of Texas Health Science Center

  • Professor Sheryl Magzamen

    Colorado State University

  • Kanza Ahmed

    UK Health Security Agency

  • Dr Anna Rom

    UK Health Security Agency

  • Talia Caplan

    Wellcome

Important information:

The framework topic documents are a final version produced as part of the SOSCHI project (Wellcome grant no. 224682/Z/21/Z). Please note that as this is an emerging topic area, indicators and methods are subject to change. Notices will be issued on this page to inform users of any changes to the information captured.

For more information on the selection criteria used for prioritising the SOSCHI topics and the development process, see the SOSCHI Framework Page .

We recommend that the proposed indicators, methods and tools (e.g. R code) described on this page can be used for official statistics reporting. See the SOSCHI Framework Page for information on the endorsement of the proposed indicators.

Last updated: 04/06/2026

Health effects of flooding

Flooding is a significant global health hazard, with far-reaching implications for public health, infrastructure, and socioeconomic stability. Climate change has significantly increased the frequency and severity of flooding events through more intense precipitation, elevated sea levels and accelerated snowmelt.

Important information:

This topic area focuses on quantifying the short-term health impacts associated with flash and fluvial floods.

Important information:

The framework topic documents are an alpha version produced as part of the SOSCHI project (Wellcome grant no. 224682/Z/21/Z). Please note that as this is an emerging topic area, indicators and methods are subject to change. Notices will be issued on this page to inform users of any changes to the information captured. For more information on the selection criteria used for prioritising the SOSCHI topics, see the SOSCHI Framework Page for more information on the development process.

The proposed indicators and methods described on this page are not fully ready for implementation within official statistics reporting. The current version has been shared in line with our open-source values – to encourage collaboration, transparency and accessibility allowing users to freely, use, modify and update these guidance materials and tools developed as part of the SOSCHI project.

Air pollution and air-borne diseases

Contents

Health effects of air pollution

The interplay between climate change and air pollution presents a pressing global health hazard with far-reaching implications for human well-being and environmental sustainability. The health impacts of air pollution by climate change are extensive and multifaceted, impacting individuals in both the short-term and long-term, encompassing a range of acute and chronic conditions.

Important information:

This topic area aims to quantify the short-term health effects of particulate matter (PM2.5) on all-cause mortality.

UN endorsement:
UN endorsement

The methods for measuring the headline outcome indicator for this topic were endorsed by the 57th United Nations Statistical Commission to include in the Global Set of Climate Change Statistics and Indicators (see decision 57/109 (b) in the Final Report ). This will be included in the Global Set metadata as:

  • Indicator 46: Climate-induced air pollution:
    46.1 Mortality attributable to short-term effects of ambient air quality (PM2.5)
Impact Pathway
Diagram showing pathways between climate
change and air pollution related health impacts. At the top left, climate drivers and hazards include rising
temperature, extreme weather events such as storms, floods, droughts, alongside increased air pollution driven by
population mobility, urbanisation and changing human behaviours. At the top right, exposure and vulnerability include
higher exposure in urban areas due to population density as well as socioeconomic and demographic factors such as age,
economic status and pre-existing health conditions. These factors interact and flow downward toward physiological
impacts and health outcomes. Physiological impacts include dehydration, increased heat stress, cardiovascular strain,
and higher infection risk. Health outcomes include acute and chronic respiratory and cardiovascular diseases, aggravated
allergies and increased premature mortality. Adaptation and mitigation measures—such as strengthened air quality
monitoring, targeted public health interventions, ecosystem-based mitigation strategies and forestation—are shown
intervening to reduce negative impacts.
Headline Indicator
Important information:

The priority indicator for the health effects of air pollution topic is all-cause mortality attributable to short-term exposure to ambient PM2.5

It was agreed to prioritise this indicator as they can provide regular, reliable, and comparable data to monitor climate-related health impacts using state-of-the-art statistical methods.

Further justification for the focus on this indicator is explained in the Topic introduction , which also outlines supplementary and additional indicators that are not in scope for the current SOSCHI framework but are recommended for future development.

The indicator has three component parts:

Important information:

Relative risk of mortality associated with short-term ambient PM2.5 exposure

Important information:

Attributable number of all-cause deaths attributable to short-term ambient PM2.5 exposure

Important information:

Attributable rate of all-cause mortality rate per 100,000 population attributable to short-term ambient PM2.5 exposure

For guidance on the process for calculating these indicator metrics, see the Methodology section below.

Policy Relevance

This indicator provides insights into how climate-related changes — particularly fine particulate matter (PM2.5)— affect air pollution health outcomes across regions and groups.

While air pollution is influenced by many factors beyond climate alone, PM2.5 is a well-established and sensitive marker of air quality-related health risk that is widely measured across countries and contexts. Estimating mortality attributable to PM2.5 helps quantify the immediate health burden of air pollution and provides evidence to support air quality regulations, emergency response planning, and public health interventions.

This indicator can therefore:

  • monitor and quantify health impacts associated with climate-sensitive air pollution exposures
  • inform national adaptation plans (NAPs) and resilience strategies
  • guide environmental and public health policy, including air quality regulation and health protection measures
Methodology

The indicator estimates short-term health effects associated with ambient PM2.5 exposure using a Generalised Additive Model (GAM), with parameters estimated by Restricted Maximum Likelihood (REML). The model adjusts for key confounders such as temperature, precipitation, humidity and wind speed, thereby isolating the specific influence of PM2.5. Lag terms are incorporated to account for the possibility that mortality may be influenced not only by same-day exposure but also by exposures on preceding days. This approach allows the model to capture both immediate and delayed health effects, providing a comprehensive assessment of the potential lagged impact of PM2.5 on all-cause mortality. Estimates are first generated at the sub-national level and subsequently aggregated to produce national totals.

Important information:
Understand the method

Read the Air pollution: methodology for details on the modelling approach, the data needed, and guidance on interpreting results.

Important information:
Develop bespoke analyses

For flexible, reproducible analysis or to adapt methods to your country or region, use the R package , which provides program code for the priority indicators.

Data Requirements and Guidance

The following data are needed for this indicator production:

  • daily all-cause mortality data from national administrative records and civil registration records
  • climate data from the National Meteorological Agency
  • population estimates from national statistical agencies

Where this data is unavailable or observations are incomplete, proxy datasets may be used. Further information on these potential sources as well as required variable names and formats are outlined in section 2 of the Air pollution: methodology

FAQs

What does all-cause mortality mean?

All-cause mortality refers to the total number of deaths in a population from any cause, without distinguishing between specific diseases or conditions. It provides a broad measure of overall population health.

In the context of this topic, all-cause mortality is used because air pollution can contribute to deaths through multiple pathways, most commonly cardiovascular and respiratory conditions.

What does “short-term exposure” to ambient PM2.5 mean?

Short-term exposure refers to exposure to ambient PM2.5 concentrations over a period of days, rather than months or years. Daily PM2.5 levels are analysed, and their effects on mortality are assessed for the same day and up to 14 previous days using lag structures.

This approach captures the short-term health effects of PM2.5 exposure and is particularly suited for identifying the impacts of pollution episodes.

What is the relevance of statistics on all-cause mortality attributable to short-term exposure to ambient PM2.5?

All-cause mortality is a comprehensive health outcome that captures deaths from any cause and is therefore a robust indicator of the overall health impact of air pollution. Short-term exposure to ambient PM2.5 has been shown to increase the risk of death, particularly from cardiovascular and respiratory causes.

Estimating mortality attributable to PM2.5 helps quantify the immediate health burden of air pollution and provides evidence to support air quality regulations, emergency response planning, and public health interventions. However, these estimates reflect population-level risk and do not imply that PM2.5 exposure is the sole cause of any individual death.

Why is PM2.5 used as the main air pollution indicator?

PM2.5 consists of very fine particles that can penetrate deep into the lungs and enter the bloodstream, making it especially harmful to human health. A substantial body of scientific evidence links short-term exposure to PM2.5 with an increased mortality risk. PM2.5 is also widely monitored and can be estimated using satellite and modelled data, which makes it suitable for consistent analysis across countries and regions.

How is the reference level for PM2.5 chosen?

By default, the topic uses the World Health Organization (WHO) 24-hour PM2.5 guideline of 15 µg/m³ as the reference level. Users may also apply their national air quality standards if these are more relevant for local policy contexts. The reference level represents a counterfactual scenario: mortality above this level is considered potentially preventable if PM2.5 concentrations were reduced to the reference value.

Why are daily data required for this analysis?

Daily data are essential because this analysis focuses on short-term health effects, which can vary from day to day. Using daily mortality, PM2.5, and meteorological data allows the model to detect rapid changes in risk following exposure. Daily data also enable flexible aggregation to weekly, monthly, or annual summaries for reporting and communication purposes.

Why are meteorological variables included in the model?

Meteorological factors such as temperature, humidity, precipitation, and wind speed influence both PM2.5 concentrations and human health. If not controlled for, they could confound the estimated relationship between PM2.5 and mortality.

Including these variables helps isolate the specific contribution of PM2.5 to mortality risk and improves the validity of the results.

Why is disaggregation by age, sex, and other characteristics important?

Disaggregating the results helps identify population groups that are more vulnerable to short-term PM2.5 exposure, such as older adults, young children, or people living in urban areas. This information supports equity-oriented public health policies and enables targeted interventions, rather than one-size-fits-all approaches.

What are the main limitations of these PM2.5 mortality estimates?

The topic estimates population-level associations and does not measure individual exposure or causation. PM2.5 exposure may be misclassified because the topic does not account for indoor air pollution or individual behaviours, such as staying indoors during high pollution days. In addition, data availability and quality can affect the precision and reliability of the estimates.

How should the results be interpreted by policymakers and the public?

The results indicate how many deaths are statistically associated with short-term PM2.5 exposure at the population level, not how many deaths were directly caused by air pollution in a deterministic sense.

These estimates are best used to identify trends, compare regions, assess the scale of the health burden, and inform air quality management and public health planning. They should be interpreted alongside other evidence and local contextual knowledge.

For broader questions that apply across the platform, please see our General FAQs section.

Related Topics

Topic Expert Group

The air pollution topic expert group was set up to review climate and health topics and guide what we measure and how we measure it. The group brings together internal and external specialists who advise on indicators and methods, share subject knowledge so we build on existing work and good practice, and help quality assure draft outputs before publication.

  • Prof. Sir Andy Haines

    London School of Hygiene & Tropical Medicine, UK

  • Prof. Ian Hamilton

    University College London (UCL), UK

  • Dr. Maquines Sewe

    Umeå University, Sweden

Important information:

The framework topic documents are a final version produced as part of the SOSCHI project (Wellcome grant no. 224682/Z/21/Z). Please note that as this is an emerging topic area, indicators and methods are subject to change. Notices will be issued on this page to inform users of any changes to the information captured.

For more information on the selection criteria used for prioritising the SOSCHI topics and the development process, see the SOSCHI Framework Page .

We recommend that the proposed indicators, methods and tools (e.g. R code) described on this page can be used for official statistics reporting. See the SOSCHI Framework Page for information on the endorsement of the proposed indicators.

Last updated: 28/05/2026

Airborne disease (CSM)

Climate change is leading to more frequent and intense high temperatures, droughts, and wildfires. These changes promote the spread of certain airborne diseases which are impacted by warm temperatures, dry conditions, dusty winds, overcrowding, and poor sanitation. One airborne disease which is particularly impacted by these conditions is Cerebrospinal Meningitis (CSM). CSM is prevalent in the African Meningitis Belt and has severe health impacts.

Methods for this topic are still in development, therefore a preliminary “Methods Review” document has been published at this stage. This document may be updated to a “Methodology” document depending on the feasibility of ongoing developments and decisions on the final scope of proposed indicators and methods.

Important information:

This topic area aims to quantify the health impacts of Cerebrospinal Meningitis (CSM) attributable to high temperatures.

Important information:

The framework topic documents are an alpha version produced as part of the SOSCHI project (Wellcome grant no. 224682/Z/21/Z). Please note that as this is an emerging topic area, indicators and methods are subject to change. Notices will be issued on this page to inform users of any changes to the information captured. For more information on the selection criteria used for prioritising the SOSCHI topics, see the SOSCHI Framework Page for more information on the development process.

The proposed indicators and methods described on this page are not fully ready for implementation within official statistics reporting. The current version has been shared in line with our open-source values – to encourage collaboration, transparency and accessibility allowing users to freely, use, modify and update these guidance materials and tools developed as part of the SOSCHI project.

Waterborne diseases

Contents

Diarrheal disease

Climate change is leading to more extreme temperatures and rainfall. These changes promote the spread of certain waterborne diseases which are impacted by extreme temperatures, contamination of waterbodies through runoff, dry conditions, water scarcity, and poor sanitation. Diarrheal disease is one of the most prevalent waterborne diseases and is highly impacted by these climatic conditions. Diarrheal disease is a public health concern particularly among young children and in regions of Africa.

Important information:

This topic area aims to quantify the health impacts of diarrheal disease attributable to extreme temperatures and rainfall.

UN endorsement:
UN endorsement

The methods for measuring the headline outcome indicator for this topic were endorsed by the 57th United Nations Statistical Commission to include in the Global Set of Climate Change Statistics and Indicators (see decision 57/109 (b) in the Final Report ). This will be included in the Global Set metadata as:

  • Indicator 44: Incidence of cases of climate-related disease:
    44.1 Incidence of diarrheal disease cases attributable to (a) heat and (b) rainfall
Impact Pathway
Diagram showing pathways between climate change
and waterborne disease (diarrhea) impacts. At the top left, climate drivers and hazards include increased frequency and
intensity of extreme weather, extreme temperatures, floods, droughts, wildfires, and storms. At the top right, exposure
and vulnerability include drinking contaminated water, flood/sewage contact, poor hygiene, and higher risk among
children, elderly populations, and communities with weak WASH symptoms. These factors interact and flow downward toward
physiological impacts and health outcomes. Physiological impacts include dehydration, malnutrition, weakened immunity,
intestinal damage, developmental delays and higher infection risk. Health outcomes include increased diarrheal disease,
malnutrition and mortality, long -term growth deficits and overburdened health systems. Adaptation and mitigation
measures—such as climate-resilient WASH infrastructure, early warning systems, emergency preparedness and community
hygiene education—are shown intervening to reduce negative impacts.
Headline Indicators
Important information:

Two priority indicators developed within the waterborne disease and water-related illnesses topic are:

  • diarrheal disease incidence attributable to extreme temperature
  • diarrheal disease incidence attributable to extreme rainfall

It was agreed to prioritise these indicators as they can provide regular, reliable, and comparable data to monitor climate-related health impacts using state-of-the-art statistical methods.

Further justification for the focus on this indicator is explained in the Topic introduction , which also outlines supplementary and additional indicators that are not in scope for the current SOSCHI framework but are recommended for future development.

Each indicator has four component parts:

Important information:

Diarrheal disease incidence attributable to extreme temperature

  • Relative risk of diarrhea cases attributable to extreme temperature
  • Number of diarrhea cases attributable to extreme temperature
  • Fraction of diarrhea cases attributable to extreme temperature
  • Diarrhea cases per 100,000 population attributable to extreme temperature
Important information:

Diarrheal disease incidence attributable to extreme rainfall

  • Relative risk of diarrhea cases attributable to extreme rainfall
  • Number of diarrhea cases attributable to extreme rainfall
  • Fraction of diarrhea cases attributable to extreme rainfall
  • Diarrhea cases per 100,000 population attributable to extreme rainfall

For guidance on the process for calculating these indicator metrics, see the Methodology section below.

Policy Relevance

These indicators can give insights into how changes in temperature and extreme rainfall events influence their risk of waterborne diseases, and how these impacts vary geographically and among the most vulnerable groups in society, informing local adaptation needs.

While diarrheal disease incidence does not capture all pathways through which climate change affects health, it is a well established and sensitive indicator of waterborne health impacts, particularly in settings with limited access to safe water, sanitation and hygiene (WASH) services.

This indicator can therefore:

  • monitor and quantify the health burden associated with extreme rainfall and extreme temperature through waterborne disease outcomes
  • inform national adaptation plans (NAPs) and resilience strategies
  • guide environmental and public health policy to reduce risks and improve outcomes
Methodology

The indicator uses epidemiological methods to examine short-term links between climate exposure and waterborne disease outcomes. The analysis uses a spatiotemporal Bayesian model combined with a Distributed Lag Nonlinear Model (DLNM). The DLNM captures both nonlinear and delayed effects of climate on monthly diarrhea counts, while the Bayesian framework accounts for spatial and temporal correlations.

Important information:
Understand the method

Read the waterborne disease and water-related illnesses: methodology for details on the modelling approach, the data needed, and guidance on interpreting results.

Important information:
Develop bespoke analyses

For flexible, reproducible analysis or to adapt methods to your country or region, use the R package , which provides program code for the priority indicators.

Important information:
Online tools for indicator analysis

Tools for selected indicators are in development. These will allow users to run quick baseline estimates and simple charts without writing code; it supports secure temporary uploads and downloadable outputs.

Data Requirements and Guidance

The following data are needed for this indicator production:

  • monthly count of diarrhea reported cases from national administrative records
  • climate data from the National Meteorological Agency
  • population estimates from national statistical agencies

Where this data is unavailable or observations are incomplete, proxy datasets may be used. Further information on these potential sources as well as required variable names and formats are outlined in section 2 of the Waterborne disease and water-related illnesses: methodology

FAQs

What is the relevance of statistics on diarrhea attributable to extreme temperature and extreme rainfall?

Diarrheal diseases are a key indicator of climate-sensitive waterborne health outcomes. Exposure to extreme temperatures and rainfall can influence diarrhea risk through multiple pathways, including pathogen survival and replication, water contamination, overload of sanitation systems, and changes in hygiene behaviour.

These indicators estimate the burden of diarrhea associated with climate conditions that increase or decrease risk at a monthly time scale, supporting climate adaptation planning, WASH interventions, and public health decision-making. Diarrhea risk is influenced by multiple interacting factors, and extreme temperatures and rainfall represent one component of this broader system.

How are extreme temperature and extreme rainfall defined for this indicator?

In the analysis, extreme temperature refers to the monthly maximum temperature, while extreme rainfall refers to the cumulative monthly rainfall. Extreme conditions are identified using relative risk (RR) rather than percentile-based thresholds. Months where RR > 1 are considered harmful, meaning the temperature or rainfall conditions are associated with increased diarrhea risk, while RR < 1 indicates protective conditions with lower risk.

The relative risk is estimated from a statistical model linking monthly diarrhea incidence to monthly maximum temperature and cumulative rainfall. Extremes, therefore, reflect health-relevant risk conditions, rather than rare values in the climate distribution. See Topic introduction for more details.

Are these direct counts of diarrhea cases caused by temperature or rainfall?

No. These are model-based attribution estimates, not direct observations of climate-caused diarrhea cases. The analysis models the association between monthly diarrhea counts and monthly maximum temperature and cumulative rainfall, while accounting for delayed and cumulative effects, and spatiotemporal variability at the monthly scale.

What does “attributable to extreme temperature or extreme rainfall” mean?

“Attributable” refers to the estimated number, rate, or fraction of diarrhea cases associated with months in which climate conditions increase risk. In this analysis, attribution is calculated only for months with a relative risk (RR) greater than 1, indicating harmful temperature or rainfall conditions. It represents the portion of the diarrhea burden that would not have occurred in the absence of these risk-increasing climate conditions, as estimated from the modeled exposure–response relationship.

What statistical methods are used to estimate diarrhea attributable to extreme temperature and extreme rainfall?

The analysis uses a spatiotemporal Bayesian model combined with a Distributed Lag Nonlinear Model (DLNM). The DLNM captures both nonlinear and delayed effects of climate on monthly diarrhea counts, while the Bayesian framework accounts for spatial and temporal correlations.

This combination enables robust estimates of relative risk and attributable burden across multiple locations over time using the R-INLA package. Depending on the dataset size and spatial coverage, running the model can take 3 to 5 minutes.

How reliable are the estimates that are produced?

The reliability of these estimates depends on the quality of monthly diarrhea case data, the representativeness of monthly maximum temperature and cumulative rainfall, and the strength of the modeled climate–diarrhea relationship.

Reliability is strengthened because the model can:

  • borrow strength across space and time, producing more stable estimates in areas or months with low case counts
  • capture delayed and nonlinear effects of temperature and rainfall on diarrhea risk, reflecting cumulative or lagged impacts rather than only immediate associations
  • account for spatial and temporal correlations, recognizing that diarrhea risk is related across neighboring regions and adjacent months
  • quantify uncertainty rigorously through credible intervals, which incorporate variability from the data, model structure, and parameter estimation

While this approach improves robustness compared with raw counts alone, users should still interpret results cautiously, particularly at sub-national scales or for smaller populations. Detailed methodological limitations are described in waterborne disease and water-related illnesses: methodology.

Are estimates available for locations or populations most at risk?

Yes, waterborne diarrhea indicators are produced at multiple spatial levels, including national, regional, and district scales, and for key sub-populations such as children under five years of age.

Estimates for the under-five population are considered reliable because diarrhea incidence is higher in this group, providing sufficient data for stable modeling. As with all analyses, uncertainty intervals (credible intervals) should still be considered when interpreting results, particularly at finer spatial scales.

For broader questions that apply across the platform, please see our General FAQs section.

Related Topics

Topic Expert Group

The waterborne disease and water-related illnesses topic expert group was set up to review this topic and guide what we measure and how we measure it. The group brings together internal and external specialists who advise on indicators and methods, share subject knowledge so we build on existing work and good practice, and help quality assure draft outputs before publication.

  • Dr. Anna Freni Sterrantino

    The Alan Turing Institute, UK

  • Dr. Kanza Ahmed

    UK Health Security Agency

  • Prof. Masahiro Hashizume

    University of Tokyo, Japan

  • Dr. Monica Pirani

    Imperial College London, UK

  • Dr. Rick Johnston

    World Health Organisation

Important information:

The framework topic documents are a final version produced as part of the SOSCHI project (Wellcome grant no. 224682/Z/21/Z). Please note that as this is an emerging topic area, indicators and methods are subject to change. Notices will be issued on this page to inform users of any changes to the information captured.

For more information on the selection criteria used for prioritising the SOSCHI topics and the development process, see the SOSCHI Framework Page .

We recommend that the proposed indicators, methods and tools (e.g. R code) described on this page can be used for official statistics reporting. See the SOSCHI Framework Page for information on the endorsement of the proposed indicators.

Last updated: 30/04/2026

Exposure to chemical contaminants

Climate change is leading to more extreme temperatures, precipitation, and weather events. These changes impact the presence of harmful chemicals in the environment through factors such as contamination of waterbodies through runoff, reduced dilution of waterbodies, and greater use of agricultural chemicals to support crop and cattle yield in warm and dry conditions. Exposure to these contaminants is linked with a range of health outcomes.

Important information:

This topic introduction provides an overview of the process we took to identify a climate-health chemical contaminants indicator.

This process identified significant limitations in data availability and knowledge within this field. As a result, the SOSCHI framework will not include an indicator on chemical contaminants. We make recommendations for future developments within the field and highlight Harmful Algal Blooms as a potential future indicator.

Important information:

The framework topic documents are an alpha version produced as part of the SOSCHI project (Wellcome grant no. 224682/Z/21/Z). Please note that as this is an emerging topic area, indicators and methods are subject to change. Notices will be issued on this page to inform users of any changes to the information captured. For more information on the selection criteria used for prioritising the SOSCHI topics, see the SOSCHI Framework Page for more information on the development process.

The proposed indicators and methods described on this page are not fully ready for implementation within official statistics reporting. The current version has been shared in line with our open-source values – to encourage collaboration, transparency and accessibility allowing users to freely, use, modify and update these guidance materials and tools developed as part of the SOSCHI project.

Vector-borne diseases

Climate change is leading to more extreme temperatures and rainfall. These changes promote the spread of certain vector-borne diseases which are impacted by warmer temperatures, humidity, and heavy rainfall. Malaria is a significant public health issue, particularly in tropical and subtropical regions, and is highly impacted by these climatic changes.

Important information:

This topic area aims to quantify the health impacts of malaria attributable to extreme temperatures and rainfall.

UN endorsement:
UN endorsement

The methods for measuring the headline outcome indicator for this topic were endorsed by the 57th United Nations Statistical Commission to include in the Global Set of Climate Change Statistics and Indicators (see decision 57/109 (b) in the Final Report ). This will be included in the Global Set metadata as:

  • Indicator 44: Incidence of cases of climate-related disease:
    44.2 Incidence of malaria cases attributable to (a) heat and (b) rainfall
Impact Pathway
Diagram showing pathways between climate
change and malaria incidence. At the top left, climate drivers and hazards include increased frequency and intensity of
extreme weather, extreme temperatures, floods, droughts and humidity shifts. At the top right, exposure and
vulnerability include proximity to breeding sites and higher mosquito biting rates, and higher risk among children,
pregnant women, and individuals with poor housing and limited healthcare access. These factors interact and flow
downward toward physiological impacts and health outcomes. Physiological impacts include fever, anemia, severe malaria
complications, pregnancy risks, organ damage, and drug resistance. Health outcomes include increased malaria cases,
hospitalisations, deaths, developmental harm in children and maternal risks. Adaptation and mitigation measures—such as
early warning systems, bed nets, spraying, community-based care, and public health education—are shown to intervene to
reduce negative impacts.
Headline Indicators
Important information:

Two priority indicators developed within the vector-borne diseases topic are:

  • malaria incidence attributable to extreme temperature
  • malaria incidence attributable to extreme rainfall

It was agreed to prioritise these indicators as they can provide regular, reliable, and comparable data to monitor climate-related health impacts using state-of-the-art statistical methods.

Further justification for the focus on this indicator is explained in the Topic introduction , which also outlines supplementary and additional indicators that are not in scope for the current SOSCHI framework but are recommended for future development.

Each indicator has four component parts:

Important information:

Malaria incidence attributable to extreme temperature

  • Relative risk of malaria cases attributable to extreme temperature
  • Number of malaria cases attributable to extreme temperature
  • Fraction of malaria cases attributable to extreme temperature
  • Malaria cases per 100,000 population attributable to extreme temperature
Important information:

Malaria incidence attributable to extreme rainfall

  • Relative risk of malaria cases attributable to extreme rainfall
  • Number of malaria cases attributable to extreme rainfall
  • Fraction of malaria cases attributable to extreme rainfall
  • Malaria cases per 100,000 population attributable to extreme rainfall

For guidance on the process for calculating these indicator metrics, see the Methodology section below.

Policy Relevance

These indicators can give insights into how changes in extreme temperature and rainfall events influence the transmission and burden of vector-borne diseases, and how these impacts vary geographically and among the most vulnerable groups in society, informing local adaptation needs.

While malaria incidence does not capture all pathways through which climate change affects health, it is a well-established and sensitive indicator of vector-borne disease risk, particularly in settings where proximity to mosquito breeding sites and high mosquito bites interact to increase transmission risk.

This indicator can therefore:

  • monitor and quantify the health burden associated with extreme rainfall and extreme temperature through vector-borne disease outcomes
  • inform national adaptation plans (NAPs) and resilience strategies
  • guide environmental and public health policy to reduce risks and improve outcomes
Methodology

The indicator uses epidemiological methods to examine short-term links between climate exposure and vector-borne disease outcomes. The analysis uses a spatiotemporal Bayesian model combined with a Distributed Lag Nonlinear Model (DLNM). This approach captures both nonlinear and delayed effects of climate on monthly malaria cases while accounting for spatial and temporal patterns in transmission.

Important information:
Understand the method

Read the vector-borne diseases: methodology for details on the modelling approach, the data needed, and guidance on interpreting results.

Important information:
Develop bespoke analyses

For flexible, reproducible analysis or to adapt methods to your country or region, use the R package , which provides program code for the priority indicators.

Important information:
Online tools for indicator analysis

Tools for selected indicators are in development. These will allow users to run quick baseline estimates and simple charts without writing code; it supports secure temporary uploads and downloadable outputs.

Data Requirements and Guidance

The following data are needed for this indicator production:

  • monthly count of malaria cases from national administrative records
  • climate data from the National Meteorological Agency
  • population estimates from national statistical agencies

Where this data is unavailable or observations are incomplete, proxy datasets may be used. Further information on these potential sources as well as required variable names and formats are outlined in section 2 of the Vector-borne diseases: Methodology

FAQs

What is the relevance of statistics on malaria attributable to extreme temperature and extreme rainfall?

Malaria is a climate-sensitive vector-borne disease, influenced by environmental conditions that affect mosquito and parasite dynamics. Variations in temperature and rainfall can alter mosquito survival, biting rates, and parasite development, thereby changing malaria transmission risk.

These indicators quantify the portion of malaria burden associated with climate conditions that increase risk on a monthly basis, helping guide vector control, public health planning, and adaptation strategies. Malaria incidence is affected by multiple factors, and climate is one component within this complex system.

How are extreme temperature and extreme rainfall defined for this indicator?

In this analysis, extreme temperature refers to the monthly maximum temperature, while extreme rainfall refers to the total monthly rainfall. Extreme conditions are determined using relative risk (RR) rather than rare or percentile-based weather events.

Months where RR > 1 are considered harmful, meaning they increase malaria risk, while RR < 1 indicates months associated with lower risk. The RR is derived from a model linking monthly malaria counts to climate conditions, so extremes represent health-relevant risk levels rather than purely unusual weather. See the Vector-borne diseases: Methodology for more details.

Are these direct counts of malaria cases caused by temperature or rainfall?

No. These are model-based attribution estimates, not observed cases directly caused by climate. The analysis evaluates the relationships between monthly malaria incidence and monthly maximum temperature and cumulative rainfall, while accounting for delayed effects and regional and seasonal variation.

What does “attributable to extreme temperature or extreme rainfall” mean?

“Attributable” indicates the number, rate, or fraction of malaria cases associated with months in which climate conditions increase risk. Attribution is calculated only for months where RR > 1, reflecting harmful temperature or rainfall conditions. It represents the estimated proportion of malaria cases that could be prevented if climate risk factors were not within the harmful temperature range (RR > 1), based on the modeled exposure-response relationship. See Vector-borne diseases: Methodology for more details.

What statistical methods are used to estimate malaria attributable to extreme temperature and extreme rainfall?

The analysis uses a spatiotemporal Bayesian modeling framework combined with a Distributed Lag Nonlinear Model (DLNM). This approach captures both nonlinear and delayed effects of climate on monthly malaria cases while accounting for spatial and temporal patterns in transmission.

The combination produces reliable relative risk and attributable burden estimates across multiple locations and months using the R-INLA package. Depending on the dataset size, running the model typically takes 3 to 5 minutes.

How reliable are the estimates that are produced?

The estimates are strengthened by the model’s ability to handle variations in malaria incidence and climate exposure across regions and months.

Key aspects of reliability include:

  • combining information across locations and time to stabilize estimates in areas or months with few cases
  • capturing delayed and nonlinear responses of malaria risk to temperature and rainfall, reflecting cumulative effects
  • accounting for spatial and temporal correlations across neighboring regions and months
  • providing uncertainty estimates through credible intervals, which incorporate data variability and model assumptions
Are estimates available for locations or populations most at risk?

Yes, malaria indicators are produced at national, regional, and district levels, as well as for key sub-populations, including children under five years of age. Estimates for the under-five population are reliable because higher case counts provide stable modeling. As with all outputs, credible intervals should be considered when interpreting results, particularly in smaller areas.

For broader questions that apply across the platform, please see our General FAQs section.

Related Topics

Topic Expert Group

The vector-borne diseases topic expert group was setup to review this topic and guide what we measure and how we measure it. The group brings together internal and external specialists who advise on indicators and methods, share subject knowledge so we build on existing work and good practice, and help quality assure draft outputs before publication.

  • Abigail Osei Owusu

    Dodowa Health Research Centre

  • Basil Tungbani

    Ghana Statistical Service

  • Dr. Billy Bauzile

    The Swiss Tropical and Public Health Institute, Switzerland

  • Dr. Cameline Orlendo

    The Swiss Tropical and Public Health Institute, Switzerland

  • Dr. Christian Selinger

    The Swiss Tropical and Public Health Institute, Switzerland

  • Dr. Eimear Cleary

    University of Southampton, UK

  • Emil K. Kpo

    Ghana Statistical Service

  • Dr. Emilie Pothin

    The Swiss Tropical and Public Health Institute, Switzerland

  • Emmanuel Adusei

    Research and Development Division, Ghana Health Service

  • Gianpaolo Pontiggia

    The Swiss Tropical and Public Health Institute, Switzerland

  • Dr. Israel Ukawuba

    The Swiss Tropical and Public Health Institute, Switzerland

  • Prof. Kofi A. Amegah

    Department of Biomedical Sciences, University of Cape Coast, Ghana

  • Prof. Louis Asiedu

    Department of Statistics & Actuarial Science, University of Ghana

  • Mary Pomaa Agyekum

    Dodowa Health Research Centre

  • Prof. Marta Blangiardo

    Imperial College London, UK

  • Dr. Monica Pirani

    Imperial College London, UK

  • Dr. Naomi Kumi

    University of Energy and Natural Resources, Sunyani, Ghana

  • Dr Patrick Ansah

    Navrongo Health Research Centre

  • Richard J. Tetteh

    Kintampo Health Research Centre

  • Solomon Nyame

    Kintampo Health Research Centre

Important information:

The framework topic documents are a final version produced as part of the SOSCHI project (Wellcome grant no. 224682/Z/21/Z). Please note that as this is an emerging topic area, indicators and methods are subject to change. Notices will be issued on this page to inform users of any changes to the information captured.

For more information on the selection criteria used for prioritising the SOSCHI topics and the development process, see the SOSCHI Framework Page .

We recommend that the proposed indicators, methods and tools (e.g. R code) described on this page can be used for official statistics reporting. See the SOSCHI Framework Page for information on the endorsement of the proposed indicators.

Last updated: 07/05/2026

Undernutrition

Climate change is leading to more extreme temperatures, precipitation, and other weather events. These changes exacerbate conditions which lead to undernutrition, a health condition resulting from an imbalance in dietary intake, where nutrients are either insufficiently or overly consumed, leading to adverse health effects. Conditions which impact undernutrition include soil fertility, crop and livestock production and diversity, food and water security, and sanitation.

Important information:

This topic area aims to quantify the health impacts of undernutrition attributable to extreme temperatures, precipitation, and drought.

Methods for this topic are still in development, therefore a preliminary “Methods Review” document has been published at this stage. This document may be updated to a “Methodology” document depending on the feasibility of ongoing developments and decisions on the final scope of proposed indicators and methods.

Important information:

The framework topic documents are an alpha version produced as part of the SOSCHI project (Wellcome grant no. 224682/Z/21/Z). Please note that as this is an emerging topic area, indicators and methods are subject to change. Notices will be issued on this page to inform users of any changes to the information captured. For more information on the selection criteria used for prioritising the SOSCHI topics, see the SOSCHI Framework Page for more information on the development process.

The proposed indicators and methods described on this page are not fully ready for implementation within official statistics reporting. The current version has been shared in line with our open-source values – to encourage collaboration, transparency and accessibility allowing users to freely, use, modify and update these guidance materials and tools developed as part of the SOSCHI project.

Mental health

Climate change is leading to more frequent and extreme climate-related hazards that influence mental health outcomes. Direct impacts on mental health can arise from increased exposure to extreme temperatures and extreme weather events. Indirect impacts can be due to displacement, malnutrition, conflict, climate-related economic and social losses, along with anxiety and distress associated with worry about climate change.

Important information:

This topic area aims to quantify the mental health impacts, currently focused on suicides attributable to extreme temperatures.

UN endorsement:
UN endorsement

The methods for measuring the headline outcome indicator for this topic were endorsed by the 57th United Nations Statistical Commission to include in the Global Set of Climate Change Statistics and Indicators (see decision 57/109 (b) in the Final Report ). This will be included in the Global Set metadata as:

  • Indicator 45: Incidence of heat and cold related illnesses or excess mortality:
    45.2 Mortality from suicide attributable to excess heat (proxy for mental health)
Impact Pathway
Diagram showing pathways between climate
change and mental health impacts. At the top left, climate drivers and hazards include increased frequency and intensity
of extreme weather, extreme temperatures, floods, droughts, wildfires, and storms. At the top right, exposure and
vulnerability include direct or repeated climate hazard exposure and socio‑economic factors such as health status,
gender, age, and occupation. These factors interact and flow downward toward physiological impacts and health outcomes.
Physiological impacts include limited labour capacity, cognitive impairment, sleep deprivation, and reduced happiness
and wellbeing. Health outcomes include PTSD, anxiety, depression, suicide, and substance abuse. Adaptation and
mitigation measures—such as health system planning, preparedness, and public health awareness campaigns—are shown
intervening to reduce negative impacts.
Headline Indicator
Important information:

The priority indicator developed within the mental health topic is suicides attributable to extreme heat.

It was agreed to prioritise this indicator as defining exposure is simpler for extreme heat than other extreme weather events, as ambient temperature data across countries and regions are generally widely available. While suicide was selected as a health outcome due to its clearer diagnostic coding and more consistent reporting compared to hospitalisations for example.

Further justification for the focus on this indicator is explained in the Topic introduction , which also outlines supplementary and additional indicators that are not in scope for the current SOSCHI framework but are recommended for future development.

The indicator has four component parts:

Important information:

Relative risk of suicide associated with temperature

Important information:

Number of suicides attributable to extreme heat

Important information:

Percentage of suicides attributable to extreme heat

Important information:

Rate of suicide per 100,000 population attributable to extreme heat

For guidance on the process for calculating these indicator metrics, see the Methodology section below.

Policy Relevance

This indicator can give insights into how more frequent and intense hot days may be impacting mental health and how this varies geographically and among the most vulnerable groups in society, informing local adaptation needs.

While suicide is not a direct measure of the incidence or prevalence of mental health conditions, it is a useful proxy for some types of mental health challenges which may be exacerbated by extreme heat.

This indicator can therefore:

  • monitor and quantify, to some extent, the mental health impacts of extreme heat
  • inform national adaptation plans (NAPs) and resilience strategies
  • guide environmental and public health policy to reduce risks and improve outcomes
Methodology

The indicator uses epidemiological methods to examine short-term links between daily temperature and suicide deaths. A time stratified case crossover design is combined with a distributed lag non-linear model (DLNM) to assess the relative risk of suicide by temperature exposure. Further estimation using this relationship is done to attribute suicides to extreme heat exposure.

Important information:
Understand the method

Read the suicides attributable to extreme heat: methodology for details on the modelling approach, the data needed, and guidance on interpreting results.

Important information:
Develop bespoke analysis

For flexible, reproducible analysis or to adapt methods to your country or region, use the R package , which provides program code for the priority indicators.

Important information:
Online tools for indicator analysis

Tools for selected indicators are in development. These will allow users to run quick baseline estimates and simple charts without writing code; it supports secure temporary uploads and downloadable outputs.

Data Requirements and Guidance

The following data are needed for this indicator production:

  • daily mortality data on suicides from national administrative records
  • population estimates from national statistical agencies
  • daily mean temperature and other optional climatic variables from government meteorological offices

Where this data is unavailable or observations are incomplete, proxy datasets may be used. Further information on these potential sources as well as required variable names and formats are outlined in section 2 of the suicides attributable to extreme heat: methodology

FAQs

What is the relevance of statistics on suicides attributable to extreme heat?

While suicide is not a direct measure of the incidence or prevalence of mental health conditions, it is a useful proxy for some types of mental health challenges which may be exacerbated by extreme heat.

These estimates can give insights into how more frequent and intense hot days may be impacting mental health and can help to inform adaptation needs. However, it is important to be aware that the exact mechanism by which heat affects the risk of suicide is not yet understood.

Why was this indicator prioritised over developing other mental health indicators?

It was agreed with our expert advisory group that the mental health impacts of extreme heat are a sensible place to start. Defining exposure is simpler for extreme heat than other extreme weather events, while ambient temperature data across countries and regions are generally widely available. Adaptation of commonly applied methods in existing studies could also be done.

Suicides as an outcome was selected to be focused on over hospitalisations due to its clearer diagnostic coding and more consistent reporting. However, it is important to be aware of national differences in suicide occurrence and recording which may relate to legal, cultural and other differences.

How can I run the indicator analysis?

The indicator analysis can be run using the online platform tool, or the ‘climatehealth’ R package. Please note that the R package provides users with more flexibility to update the parameters specified in the analysis pipeline. Please see the suicides attributable to extreme heat: methodology for more detail.

Can I use weekly or monthly data?

Due to the nature of the case-crossover methodology, the indicator will only work with daily input data.

How is extreme heat defined?

As a default in the model, extreme heat is defined as days where the temperature was in the top 2.5% (97.5th percentile and above) of daily temperatures. This is based on the temperature distribution over the whole time series provided for each geographical area. The word ‘extreme’ therefore refers to the relative rarity of these higher temperatures to the corresponding area, not to an absolute value, which would vary across the world.

Are these direct counts of suicides caused by heat?

No, these are estimates based on a statistical model. These are produced by modelling the association between daily suicide occurrences and daily mean temperature. This association is then used to estimate the attribution to extreme heat. As these are modelled estimates there are uncertainty around the statistics that should be considered in any interpretation of results.

What does 'attributable to extreme heat' mean in this context?

Dependent on the type of estimate, this is the number, rate (per 100,000 population) or proportion of suicides that would not have occurred if there had been no exposure to extreme heat.

It is based on the risk of suicide from the modelled temperature-suicide association above the defined threshold of extreme heat. This threshold can be altered by a user if needed to accommodate differing relationships.

What do negative attributable numbers mean?

A negative attributable number can suggest that, in the context of the model, extreme heat is associated with a reduction in suicide rates, indicating an inverse relationship. Though any uncertainty around these estimates should be considered in this interpretation.

How reliable are the estimates that are produced?

The analysis uses daily suicide counts to model temperature-related impacts. As suicide is generally relatively infrequent as a cause of death in the population as a whole, numbers can be low, especially at sub-national levels, contributing to uncertainty around the estimates. Confidence intervals and statistics on model validation should be considered when interpreting results.

More information on data and methodological limitations can be found in suicides attributable to extreme heat: methodology

Are there estimates available looking at populations most at risk?

Users can run the analysis on sub-populations such as by age group or sex. This is providing they have the relevant variables, as set out in the data template in suicides attributable to extreme heat: methodology

However, users should be aware that breaking down estimates into smaller groups can limit the reliability of statistical modelling and potentially lead to wide uncertainty in the estimates

For broader questions that apply across the platform, please see our General FAQs section.

Related Topics

Topic Expert Group

The mental health topic expert group is one of ten groups set up during discovery to review climate and health topics and guide what we measure and how we measure it. The group brings together internal and external specialists who advise on indicators and methods, share subject knowledge so we build on existing work and good practice, and help quality assure draft outputs before publication.

  • Dr. Alessandro Massazza

    United for Global Mental Health

  • Prof. Masahiro Hashizume

    University of Tokyo, Japan

  • Dr. Yoonhee Kim

    University of Tokyo, Japan

  • Dr. Elaine Flores Ramos

    London School of Hygiene and Tropical Medicine, UK

  • Dr. Kelton Minor

    University of Copengagen

  • Dr. Anya Gopfert

    UK Health Security Agency

  • Prof. Julian Eaton

    London School of Hygiene and Tropical Medicine, UK

  • Prof. Sonja Ayeb Karlsson

    University College London (UCL), UK

  • Dr. Joshua Wortzel

    Yale School of Medicine, USA

  • Prof. Ann John

    Swansea University, UK

  • Dr. Emma Lawrance

    Imperial College London, UK

  • Dr. Piumee Bandara

    World Health Organisation (WHO)

  • Dr. Sandersan Onie

    World Health Organisation (WHO)

  • Kanza Ahmed

    UK Health Security Agency

  • Dr. Lisa Page

    Brighton and Sussex Medical School, UK

  • Dr. Isabel Fletcher

    Wellcome

  • Jessica Newberry Le Vay

    University of Oxford, UK

  • Dr. Emma Sharland

    Office for National Statistics, UK

  • Klaudia Rzepnicka

    Office for National Statistics, UK

Important information:

The framework topic documents are a final version produced as part of the SOSCHI project (Wellcome grant no. 224682/Z/21/Z). Please note that as this is an emerging topic area, indicators and methods are subject to change. Notices will be issued on this page to inform users of any changes to the information captured.

For more information on the selection criteria used for prioritising the SOSCHI topics and the development process, see the SOSCHI Framework Page .

We recommend that the proposed indicators, methods and tools (e.g. R code) described on this page can be used for official statistics reporting. See the SOSCHI Framework Page for information on the endorsement of the proposed indicators.

Last updated: 21/05/2026

Healthcare systems and facilities

Healthcare systems include a broad range of activities from public health initiatives to services, covering both private and public sectors. Globally, healthcare systems are under significant pressure which are further compounded by the effects of climate change. These can be direct impacts to infrastructure as well as disruption to medical supply and service delivery.

The ability of facilities to function, particularly in vulnerable regions, during extreme conditions such as flooding, heatwaves and storms determines the effectiveness of these systems in mitigating the impacts of climate change on public health.

Important information:

This topic area follows a different approach to the wider framework, aiming to use qualitative methods to assess the impact on health workforce, infrastructure and technology as well as service delivery.

Health care systems illustration
Important information:

The framework topic documents are an alpha version produced as part of the SOSCHI project (Wellcome grant no. 224682/Z/21/Z). Please note that as this is an emerging topic area, indicators and methods are subject to change. Notices will be issued on this page to inform users of any changes to the information captured. For more information on the selection criteria used for prioritising the SOSCHI topics, see the SOSCHI Framework Page for more information on the development process.

The proposed indicators and methods described on this page are not fully ready for implementation within official statistics reporting. The current version has been shared in line with our open-source values – to encourage collaboration, transparency and accessibility allowing users to freely, use, modify and update these guidance materials and tools developed as part of the SOSCHI project.