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Disease burden

Disease burden is the impact of a health problem as measured by financial cost, mortality, morbidity, or other indicators. It is often quantified in terms of quality-adjusted life years (QALYs) or disability-adjusted life years (DALYs). Both of these metrics quantify the number of years lost due to disability (YLDs), sometimes also known as years lost due to disease or years lived with disability/disease.[1] One DALY can be thought of as one year of healthy life lost, and the overall disease burden can be thought of as a measure of the gap between current health status and the ideal health status (where the individual lives to old age without disease and disability).[2][3][4] According to an article published in The Lancet in June 2015, low back pain and major depressive disorder were among the top ten causes of YLDs and were the cause of more health loss than diabetes, chronic obstructive pulmonary disease, and asthma combined. The study based on data from 188 countries, considered to be the largest and most detailed analysis to quantify levels, patterns, and trends in ill health and disability, concluded that "the proportion of disability-adjusted life years due to YLDs increased globally from 21.1% in 1990 to 31.2% in 2013."[5] The environmental burden of disease is defined as the number of DALYs that can be attributed to environmental factors.[4][6][7] Similarly, the work-related burden of disease is defined as the number of deaths and DALYs that can be attributed to occupational risk factors to human health.[8] These measures allow for comparison of disease burdens, and have also been used to forecast the possible impacts of health interventions. By 2014, DALYs per head were "40% higher in low-income and middle-income regions."[9]

Burden of all infectious diseases, worldwide in 2004, measured in disability-adjusted life years
Burden of non-communicable diseases, worldwide in 2004, measured in disability-adjusted life years

The World Health Organization (WHO) has provided a set of detailed guidelines for measuring disease burden at the local or national level.[4] In 2004, the health issue leading to the highest YLD for both men and women was unipolar depression;[10] in 2010, it was lower back pain.[11] According to an article in The Lancet published in November 2014, disorders in those aged 60 years and older represent "23% of the total global burden of disease" and leading contributors to disease burden in this group in 2014 were "cardiovascular diseases (30.3%), malignant neoplasms (15.1%), chronic respiratory diseases (9.5%), musculoskeletal diseases (7.5%), and neurological and mental disorders (6.6%)."[9]: 549 

Statistics edit

The first study on the global burden of disease, conducted in 1990, quantified the health effects of more than 100 diseases and injuries for eight regions of the world, giving estimates of morbidity and mortality by age, sex, and region. It also introduced the DALY as a new metric to quantify the burden of diseases, injuries, and risk factors.[4][12][13] From 2000 to 2002, the 1990 study was updated to include a more extensive analysis using a framework known as comparative risk factor assessment.[12]

In 2004, the World Health Organization calculated that 1.5 billion disability-adjusted life years were lost to disease and injury.[14][15]

Disease category Percent of all YPLLs, worldwide[15] Percent of all DALYs, worldwide[14] Percent of all YPLLs, Europe[15] Percent of all DALYs, Europe[14] Percent of all YPLLs, US and Canada[15] Percent of all DALYs, US and Canada[14]
Infectious and parasitic diseases, especially lower respiratory tract infections, diarrhea, AIDS, tuberculosis, and malaria 37% 26% 9% 6% 5% 3%
Neuropsychiatric conditions, such as depression 2% 13% 3% 19% 5% 28%
Injuries, especially motor vehicle accidents 14% 12% 18% 13% 18% 10%
Cardiovascular diseases, principally heart attacks and stroke 14% 10% 35% 23% 26% 14%
Premature birth and other perinatal deaths (infant mortality) 11% 8% 4% 2% 3% 2%
Cancer 8% 5% 19% 11% 25% 13%

Modifiable risk factors edit

In 2006, the WHO released a report which addressed the amount of global disease that could be prevented by reducing environmental risk factors.[6] The report found that approximately one-fourth of the global disease burden and more than one-third of the burden among children was due to modifiable environmental factors. The "environmentally-mediated" disease burden is much higher in developing countries, with the exception of certain non-communicable diseases, such as cardiovascular diseases and cancers, where the per capita disease burden is larger in developed countries. Children have the highest death toll, with more than 4 million environmentally-caused deaths yearly, mostly in developing countries. The infant death rate attributed to environmental causes is also 12 times higher in developing countries. 85 out of the 102 major diseases and injuries classified by WHO were due to environmental factors.[6]

To measure the environmental health impact, environment was defined as "all the physical, chemical and biological factors external to a person, and all the related behaviours".[16] The definition of modifiable environment included:

Certain environmental factors were excluded from this definition:

Methodology edit

The WHO developed a methodology to quantify the health of a population using summary measures, which combine information on mortality and non-fatal health outcomes. The measures quantify either health gaps or health expectancies; the most commonly used health summary measure is the DALY.[3][13][18]

The exposure-based approach, which measures exposure via pollutant levels, is used to calculate the environmental burden of disease.[20] This approach requires knowledge of the outcomes associated with the relevant risk factor, exposure levels and distribution in the study population, and dose-response relationships of the pollutants.

A dose-response relationship is a function of the exposure parameter assessed for the study population.[3] Exposure distribution and dose-response relationships are combined to yield the study population's health impact distribution, usually expressed in terms of incidence. The health impact distribution can then be converted into health summary measures, such as DALYs. Exposure-response relationships for a given risk factor are commonly obtained from epidemiological studies.[3][4] For example, the disease burden of outdoor air pollution for Santiago, Chile, was calculated by measuring the concentration of atmospheric particulate matter (PM10), estimating the susceptible population, and combining these data with relevant dose-response relationships. A reduction of particulate matter levels in the air to recommended standards would cause a reduction of about 5,200 deaths, 4,700 respiratory hospital admissions, and 13,500,000 days of restricted activity per year, for a total population of 4.7 million.[3]

In 2002, the WHO estimated the global environmental burden of disease by using risk assessment data to develop environmentally attributable fractions (EAFs) of mortality and morbidity for 85 categories of disease.[3][4][21] In 2007, they released the first country-by-country analysis of the impact environmental factors had on health for its then 192 member states. These country estimates were the first step to assist governments in carrying out preventive action. The country estimates were divided into three parts:

Environmental burden of disease for selected risk factors
This presents the yearly burden, expressed in deaths and DALYs, attributable to: indoor air pollution from solid fuel use; outdoor air pollution; and unsafe water, sanitation, and hygiene. Results are calculated using the exposure-based approach.
Total environmental burden of disease for the relevant country
The total number of deaths, DALYs per capita, and the percentage of the national burden of disease attributable to the environment represent the disease burden that could be avoided by modifying the environment as a whole.
Environmental burden by disease category
Each country summary was broken down by the disease group, where the annual number of DALYs per capita attributable to environmental factors were calculated for each group.[4]

Implementation and interpretation edit

The public health impacts of air pollution (annual means of PM10 and ozone), noise pollution, and radiation (radon and UV), can be quantified using DALYs. For each disease, a DALY is calculated as:

DALYs = number of people with the disease × duration of the disease (or loss of life expectancy in the case of mortality) × severity (varying from 0 for perfect health to 1 for death)

Necessary data include prevalence data, exposure-response relationships, and weighting factors that give an indication of the severity of a certain disorder. When information is missing or vague, experts will be consulted in order to decide which alternative data sources to use. An uncertainty analysis is carried out so as to analyze the effects of different assumptions.[20][22][23][24]

Uncertainty edit

When estimating the environmental burden of disease, a number of potential sources of error may arise in the measure of exposure and exposure-risk relationship, assumptions made in applying the exposure or exposure-risk relationship to the relevant country, health statistics, and, if used, expert opinions.

Generally, it is not possible to estimate a formal confidence interval, but it is possible to estimate a range of possible values the environmental disease burden may take based on different input parameters and assumptions.[3][4][6] When more than one definition has to be made about a certain element in the assessment, multiple analyses can be run, using different sets of definitions. Sensitivity and decision analyses can help determine which sources of uncertainty affect the final results the most.[6]

Examples edit

The Netherlands edit

In the Netherlands, air pollution is associated with respiratory and cardiovascular diseases, and exposure to certain forms of radiation can lead to the development of cancer. Quantification of the health impact of the environment was done by calculating DALYs for air pollution, noise, radon, UV, and indoor dampness for the period 1980 to 2020. In the Netherlands, 2–5% of the total disease burden in 2000 could be attributed to the effects of (short-term) exposure to air pollution, noise, radon, natural UV radiation, and dampness in houses. The percentage can increase to up to 13% due to uncertainty, assuming no threshold.

Among the investigated factors, long-term PM10 exposure have the greatest impact on public health. As levels of PM10 decrease, related disease burden is also expected to decrease. Noise exposure and its associated disease burden is likely to increase to a level where the disease burden is similar to that of traffic accidents. The rough estimates do not provide a complete picture of the environmental health burden, because data are uncertain, not all environmental-health relationships are known, not all environmental factors have been included, and it was not possible to assess all potential health effects. The effects of a number of these assumptions were evaluated in an uncertainty analysis.[20]

Canada edit

Exposure to environmental hazards may cause chronic diseases, so the magnitude of their contribution to Canada's total disease burden is not well understood. In order to give an initial estimate of the environmental burden of disease for four major categories of disease, the EAF developed by the WHO, EAFs developed by other researchers, and data from Canadian public health institutions were used.[25] Results showed a total of 10,000–25,000 deaths, with 78,000–194,000 hospitalizations; 600,000–1.5 million days spent in hospital; 1.1–1.8 million restricted activity days for individuals with asthma; 8000–24,000 new cases of cancer; 500–2,500 babies with low birth weights; and C$3.6–9.1 billion in costs each year due to respiratory disease, cardiovascular illness, cancer, and congenital conditions associated with adverse environmental exposures.[25]

Burden of disease attributable to lack of water, sanitation, hygiene edit

The WHO has investigated which proportion of death and disease worldwide can be attributed to insufficient WASH services. In their analysis they focus on the following four health outcomes: diarrhea, acute respiratory infections, undernutrition, and soil-transmitted helminthiases (STHs).[26]: vi  These health outcomes are also included as an indicator for achieving Sustainable Development Goal 3 ("Good Health and Wellbeing"): Indicator 3.9.2 reports on the "mortality rate attributed to unsafe water, sanitation, and lack of hygiene".

In 2023, WHO summarized the available data with the following key findings: "In 2019, use of safe WASH services could have prevented the loss of at least 1.4 million lives and 74 million disability-adjusted life years (DALYs) from four health outcomes. This represents 2.5% of all deaths and 2.9% of all DALYs globally."[26]: vi  Of the four health outcomes studied, it was diarrheal disease that had the most striking correlation, namely the highest number of "attributable burden of disease": over 1 million deaths and 55 million DALYs from diarrheal diseases was linked with lack of WASH. Of these deaths, 564,000 deaths were linked to unsafe sanitation in particular.

Acute respiratory infections was the second largest cause of WASH-attributable burden of disease in 2019, followed by undernutrition and soil-transmitted helminthiases. The latter does not lead to such high death numbers (in comparison) but is fully connected to unsafe WASH: its "population-attributable fraction" is estimated to be 100%.[26]: vi 

The connection between lack of WASH and burden of disease is primarily one of poverty and poor access in developing countries: "the WASH-attributable mortality rates were 42, 30, 4.4 and 3.7 deaths per 100 000 population in low-income, lower-middle income, upper-middle income and high-income countries, respectively."[26]: vi  The regions most affected are in the WHO Africa and South-East Asia regions. Here, between 66 and 76% of the diarrheal disease burden could be prevented if access to safe WASH services was provided.[26]: vi 

Most of the diseases resulting from lack of sanitation have a direct relation to poverty. For example, open defecation – which is the most extreme form of "lack of sanitation" – is a major factor in causing various diseases, most notably diarrhea and intestinal worm infections.[27][28]

An earlier report by World Health Organization which analyzed data up to 2016 had found higher values: "The WASH-attributable disease burden amounts to 3.3% of global deaths and 4.6% of global DALYs. Among children under 5 years, WASH-attributable deaths represent 13% of deaths and 12% of DALYs. Worldwide, 1.9 million deaths and 123 million DALYs could have been prevented in 2016 with adequate WASH."[29] An even earlier study from 2002 had estimated even higher values, namely that up to 5 million people die each year from preventable waterborne diseases.[30] These changes in the estimates of death and disease can partly be explained by the progress that has been achieved in some countries in improving access to WASH. For example, several large Asian countries (China, India, Indonesia) have managed to increase the "safely managed sanitation services" in their country from the year 2015 to 2020 by more than 10 percentage points.[26]: 26 

Criticism edit

There is no consensus on the best measures of the public's health. This is not surprising because measurements are used to accomplish diverse functions (e.g., population health assessment, evaluation of the effectiveness of interventions, formulation of health policies, and projection of future resource need). The choice of measures may also depend on individual and societal values. Measures that only consider premature death will omit the burden of living with a disease or disability, and measures that combine both in a single measure (i.e. DALYs) need to make a judgment to the significance of these measures compared to each other. Other metrics such as economic costs will not capture pain and suffering or other broader aspects of burden.[31]

DALYs are a simplification of a complex reality, and therefore only give a crude indication of environmental health impact. Relying on DALYs may make donors take a narrow approach to health care programs. Foreign aid is most often directed at diseases with the highest DALYs, ignoring the fact that other diseases, despite having lower DALYs, are still major contributors to disease burden. Less-publicized diseases thus have little or no funding for health efforts. For example, maternal death (one of the top three killers in most poor countries) and pediatric respiratory and intestinal infections maintain a high disease burden, and safe pregnancy and the prevention of coughs in infants do not receive adequate funding.[32]

See also edit

References edit

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  5. ^ Global Burden of Disease Study 2013 Collaborators (8 June 2015). "Global, regional, and national incidence, prevalence, and years lived with disability for 301 acute and chronic diseases and injuries in 188 countries, 1990–2013: a systematic analysis for the Global Burden of Disease Study 2013". The Lancet. 386 (9995): 743–800. doi:10.1016/S0140-6736(15)60692-4. PMC 4561509. PMID 26063472. {{cite journal}}: |author1= has generic name (help)CS1 maint: numeric names: authors list (link)
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Sources edit

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  • . Health statistics and health information systems. World Health Organization. Archived from the original on November 14, 2008.
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  • Prüss, Annette; Havelaar, Arie (2001). Fewtrell, Lorna; Bartram, Jamie (eds.). "The Global Burden of Disease study and applications in water, sanitation and hygiene" (PDF). Water Quality: Guidelines, Standards and Health. London: IWA Publishing.
  • "The WHO guides on assessing the environmental burden of disease" (PDF). World Health Organization.

disease, burden, global, burden, disease, redirects, here, research, program, that, measures, disease, burden, global, burden, disease, study, confused, with, environmental, disease, impact, health, problem, measured, financial, cost, mortality, morbidity, oth. Global burden of disease redirects here For the research program that measures disease burden see Global Burden of Disease Study Not to be confused with Environmental disease Disease burden is the impact of a health problem as measured by financial cost mortality morbidity or other indicators It is often quantified in terms of quality adjusted life years QALYs or disability adjusted life years DALYs Both of these metrics quantify the number of years lost due to disability YLDs sometimes also known as years lost due to disease or years lived with disability disease 1 One DALY can be thought of as one year of healthy life lost and the overall disease burden can be thought of as a measure of the gap between current health status and the ideal health status where the individual lives to old age without disease and disability 2 3 4 According to an article published in The Lancet in June 2015 low back pain and major depressive disorder were among the top ten causes of YLDs and were the cause of more health loss than diabetes chronic obstructive pulmonary disease and asthma combined The study based on data from 188 countries considered to be the largest and most detailed analysis to quantify levels patterns and trends in ill health and disability concluded that the proportion of disability adjusted life years due to YLDs increased globally from 21 1 in 1990 to 31 2 in 2013 5 The environmental burden of diseaseis defined as the number of DALYs that can be attributed to environmental factors 4 6 7 Similarly the work related burden of diseaseis defined as the number of deaths and DALYs that can be attributed to occupational risk factors to human health 8 These measures allow for comparison of disease burdens and have also been used to forecast the possible impacts of health interventions By 2014 DALYs per head were 40 higher in low income and middle income regions 9 Burden of all infectious diseases worldwide in 2004 measured in disability adjusted life yearsBurden of non communicable diseases worldwide in 2004 measured in disability adjusted life yearsThe World Health Organization WHO has provided a set of detailed guidelines for measuring disease burden at the local or national level 4 In 2004 the health issue leading to the highest YLD for both men and women was unipolar depression 10 in 2010 it was lower back pain 11 According to an article in The Lancet published in November 2014 disorders in those aged 60 years and older represent 23 of the total global burden of disease and leading contributors to disease burden in this group in 2014 were cardiovascular diseases 30 3 malignant neoplasms 15 1 chronic respiratory diseases 9 5 musculoskeletal diseases 7 5 and neurological and mental disorders 6 6 9 549 Contents 1 Statistics 2 Modifiable risk factors 3 Methodology 4 Implementation and interpretation 4 1 Uncertainty 5 Examples 5 1 The Netherlands 5 2 Canada 5 3 Burden of disease attributable to lack of water sanitation hygiene 6 Criticism 7 See also 8 References 8 1 SourcesStatistics editThe first study on the global burden of disease conducted in 1990 quantified the health effects of more than 100 diseases and injuries for eight regions of the world giving estimates of morbidity and mortality by age sex and region It also introduced the DALY as a new metric to quantify the burden of diseases injuries and risk factors 4 12 13 From 2000 to 2002 the 1990 study was updated to include a more extensive analysis using a framework known as comparative risk factor assessment 12 In 2004 the World Health Organization calculated that 1 5 billion disability adjusted life years were lost to disease and injury 14 15 Disease category Percent of all YPLLs worldwide 15 Percent of all DALYs worldwide 14 Percent of all YPLLs Europe 15 Percent of all DALYs Europe 14 Percent of all YPLLs US and Canada 15 Percent of all DALYs US and Canada 14 Infectious and parasitic diseases especially lower respiratory tract infections diarrhea AIDS tuberculosis and malaria 37 26 9 6 5 3 Neuropsychiatric conditions such as depression 2 13 3 19 5 28 Injuries especially motor vehicle accidents 14 12 18 13 18 10 Cardiovascular diseases principally heart attacks and stroke 14 10 35 23 26 14 Premature birth and other perinatal deaths infant mortality 11 8 4 2 3 2 Cancer 8 5 19 11 25 13 Modifiable risk factors editIn 2006 the WHO released a report which addressed the amount of global disease that could be prevented by reducing environmental risk factors 6 The report found that approximately one fourth of the global disease burden and more than one third of the burden among children was due to modifiable environmental factors The environmentally mediated disease burden is much higher in developing countries with the exception of certain non communicable diseases such as cardiovascular diseases and cancers where the per capita disease burden is larger in developed countries Children have the highest death toll with more than 4 million environmentally caused deaths yearly mostly in developing countries The infant death rate attributed to environmental causes is also 12 times higher in developing countries 85 out of the 102 major diseases and injuries classified by WHO were due to environmental factors 6 To measure the environmental health impact environment was defined as all the physical chemical and biological factors external to a person and all the related behaviours 16 The definition of modifiable environment included Air soil and water pollution with chemicals or biological agents Ultraviolet and ionizing radiation Noise and electromagnetic fields Built environment Agricultural methods and irrigation schemes Human made climate change and ecosystem degradation Occupational risks including exposure to long working hours 17 Individual behaviors such as hand washing and food contamination due to unsafe water or dirty hands 16 18 Certain environmental factors were excluded from this definition Indoor smoke from solid fuel use Lead Mercury 19 Natural climate change as opposed to human caused climate change Occupational airborne particulates or carcinogens Outdoor air pollution Sanitation and hygiene problems Second hand smoke Solar ultraviolet radiationMethodology editThe WHO developed a methodology to quantify the health of a population using summary measures which combine information on mortality and non fatal health outcomes The measures quantify either health gaps or health expectancies the most commonly used health summary measure is the DALY 3 13 18 The exposure based approach which measures exposure via pollutant levels is used to calculate the environmental burden of disease 20 This approach requires knowledge of the outcomes associated with the relevant risk factor exposure levels and distribution in the study population and dose response relationships of the pollutants A dose response relationship is a function of the exposure parameter assessed for the study population 3 Exposure distribution and dose response relationships are combined to yield the study population s health impact distribution usually expressed in terms of incidence The health impact distribution can then be converted into health summary measures such as DALYs Exposure response relationships for a given risk factor are commonly obtained from epidemiological studies 3 4 For example the disease burden of outdoor air pollution for Santiago Chile was calculated by measuring the concentration of atmospheric particulate matter PM10 estimating the susceptible population and combining these data with relevant dose response relationships A reduction of particulate matter levels in the air to recommended standards would cause a reduction of about 5 200 deaths 4 700 respiratory hospital admissions and 13 500 000 days of restricted activity per year for a total population of 4 7 million 3 In 2002 the WHO estimated the global environmental burden of disease by using risk assessment data to develop environmentally attributable fractions EAFs of mortality and morbidity for 85 categories of disease 3 4 21 In 2007 they released the first country by country analysis of the impact environmental factors had on health for its then 192 member states These country estimates were the first step to assist governments in carrying out preventive action The country estimates were divided into three parts Environmental burden of disease for selected risk factors This presents the yearly burden expressed in deaths and DALYs attributable to indoor air pollution from solid fuel use outdoor air pollution and unsafe water sanitation and hygiene Results are calculated using the exposure based approach Total environmental burden of disease for the relevant country The total number of deaths DALYs per capita and the percentage of the national burden of disease attributable to the environment represent the disease burden that could be avoided by modifying the environment as a whole Environmental burden by disease category Each country summary was broken down by the disease group where the annual number of DALYs per capita attributable to environmental factors were calculated for each group 4 Implementation and interpretation editThe public health impacts of air pollution annual means of PM10 and ozone noise pollution and radiation radon and UV can be quantified using DALYs For each disease a DALY is calculated as DALYs number of people with the disease duration of the disease or loss of life expectancy in the case of mortality severity varying from 0 for perfect health to 1 for death Necessary data include prevalence data exposure response relationships and weighting factors that give an indication of the severity of a certain disorder When information is missing or vague experts will be consulted in order to decide which alternative data sources to use An uncertainty analysis is carried out so as to analyze the effects of different assumptions 20 22 23 24 Uncertainty edit When estimating the environmental burden of disease a number of potential sources of error may arise in the measure of exposure and exposure risk relationship assumptions made in applying the exposure or exposure risk relationship to the relevant country health statistics and if used expert opinions Generally it is not possible to estimate a formal confidence interval but it is possible to estimate a range of possible values the environmental disease burden may take based on different input parameters and assumptions 3 4 6 When more than one definition has to be made about a certain element in the assessment multiple analyses can be run using different sets of definitions Sensitivity and decision analyses can help determine which sources of uncertainty affect the final results the most 6 Examples editThe Netherlands edit In the Netherlands air pollution is associated with respiratory and cardiovascular diseases and exposure to certain forms of radiation can lead to the development of cancer Quantification of the health impact of the environment was done by calculating DALYs for air pollution noise radon UV and indoor dampness for the period 1980 to 2020 In the Netherlands 2 5 of the total disease burden in 2000 could be attributed to the effects of short term exposure to air pollution noise radon natural UV radiation and dampness in houses The percentage can increase to up to 13 due to uncertainty assuming no threshold Among the investigated factors long term PM10 exposure have the greatest impact on public health As levels of PM10 decrease related disease burden is also expected to decrease Noise exposure and its associated disease burden is likely to increase to a level where the disease burden is similar to that of traffic accidents The rough estimates do not provide a complete picture of the environmental health burden because data are uncertain not all environmental health relationships are known not all environmental factors have been included and it was not possible to assess all potential health effects The effects of a number of these assumptions were evaluated in an uncertainty analysis 20 Canada edit Exposure to environmental hazards may cause chronic diseases so the magnitude of their contribution to Canada s total disease burden is not well understood In order to give an initial estimate of the environmental burden of disease for four major categories of disease the EAF developed by the WHO EAFs developed by other researchers and data from Canadian public health institutions were used 25 Results showed a total of 10 000 25 000 deaths with 78 000 194 000 hospitalizations 600 000 1 5 million days spent in hospital 1 1 1 8 million restricted activity days for individuals with asthma 8000 24 000 new cases of cancer 500 2 500 babies with low birth weights and C 3 6 9 1 billion in costs each year due to respiratory disease cardiovascular illness cancer and congenital conditions associated with adverse environmental exposures 25 Burden of disease attributable to lack of water sanitation hygiene edit This section is an excerpt from WASH WASH attributable burden of diseases and injuries edit The WHO has investigated which proportion of death and disease worldwide can be attributed to insufficient WASH services In their analysis they focus on the following four health outcomes diarrhea acute respiratory infections undernutrition and soil transmitted helminthiases STHs 26 vi These health outcomes are also included as an indicator for achieving Sustainable Development Goal 3 Good Health and Wellbeing Indicator 3 9 2 reports on the mortality rate attributed to unsafe water sanitation and lack of hygiene In 2023 WHO summarized the available data with the following key findings In 2019 use of safe WASH services could have prevented the loss of at least 1 4 million lives and 74 million disability adjusted life years DALYs from four health outcomes This represents 2 5 of all deaths and 2 9 of all DALYs globally 26 vi Of the four health outcomes studied it was diarrheal disease that had the most striking correlation namely the highest number of attributable burden of disease over 1 million deaths and 55 million DALYs from diarrheal diseases was linked with lack of WASH Of these deaths 564 000 deaths were linked to unsafe sanitation in particular Acute respiratory infections was the second largest cause of WASH attributable burden of disease in 2019 followed by undernutrition and soil transmitted helminthiases The latter does not lead to such high death numbers in comparison but is fully connected to unsafe WASH its population attributable fraction is estimated to be 100 26 vi The connection between lack of WASH and burden of disease is primarily one of poverty and poor access in developing countries the WASH attributable mortality rates were 42 30 4 4 and 3 7 deaths per 100 000 population in low income lower middle income upper middle income and high income countries respectively 26 vi The regions most affected are in the WHO Africa and South East Asia regions Here between 66 and 76 of the diarrheal disease burden could be prevented if access to safe WASH services was provided 26 vi Most of the diseases resulting from lack of sanitation have a direct relation to poverty For example open defecation which is the most extreme form of lack of sanitation is a major factor in causing various diseases most notably diarrhea and intestinal worm infections 27 28 An earlier report by World Health Organization which analyzed data up to 2016 had found higher values The WASH attributable disease burden amounts to 3 3 of global deaths and 4 6 of global DALYs Among children under 5 years WASH attributable deaths represent 13 of deaths and 12 of DALYs Worldwide 1 9 million deaths and 123 million DALYs could have been prevented in 2016 with adequate WASH 29 An even earlier study from 2002 had estimated even higher values namely that up to 5 million people die each year from preventable waterborne diseases 30 These changes in the estimates of death and disease can partly be explained by the progress that has been achieved in some countries in improving access to WASH For example several large Asian countries China India Indonesia have managed to increase the safely managed sanitation services in their country from the year 2015 to 2020 by more than 10 percentage points 26 26 Criticism editThere is no consensus on the best measures of the public s health This is not surprising because measurements are used to accomplish diverse functions e g population health assessment evaluation of the effectiveness of interventions formulation of health policies and projection of future resource need The choice of measures may also depend on individual and societal values Measures that only consider premature death will omit the burden of living with a disease or disability and measures that combine both in a single measure i e DALYs need to make a judgment to the significance of these measures compared to each other Other metrics such as economic costs will not capture pain and suffering or other broader aspects of burden 31 DALYs are a simplification of a complex reality and therefore only give a crude indication of environmental health impact Relying on DALYs may make donors take a narrow approach to health care programs Foreign aid is most often directed at diseases with the highest DALYs ignoring the fact that other diseases despite having lower DALYs are still major contributors to disease burden Less publicized diseases thus have little or no funding for health efforts For example maternal death one of the top three killers in most poor countries and pediatric respiratory and intestinal infections maintain a high disease burden and safe pregnancy and the prevention of coughs in infants do not receive adequate funding 32 See also editClimate change and infectious diseases Vectorborne diseases WASH water sanitation and hygiene Waterborne diseasesReferences edit WHO Metrics Disability Adjusted Life Year DALY WHO Retrieved 2020 01 02 Pruss Ustun Annette Corvalan Carlos 2006 Preventing disease through healthy environments Towards an estimate of the environmental burden of disease PDF Quantifying environmental health impacts World Health Organization a b c d e f g Kay David Pruss Annette Corvalan Carlos 23 24 August 2000 Methodology for assessment of Environmental burden of disease PDF ISEE session on environmental burden of disease Buffalo a b c d e f g h Pruss Ustun Annette Mathers C Corvalan Carlos Woodward A 2003 Assessing the environmental burden of disease at national and local levels Introduction and methods WHO Environmental Burden of Disease Series Vol 1 Geneva World Health Organization ISBN 978 9241546201 Archived from the original on June 12 2005 Global Burden of Disease Study 2013 Collaborators 8 June 2015 Global regional and national incidence prevalence and years lived with disability for 301 acute and chronic diseases and injuries in 188 countries 1990 2013 a systematic analysis for the Global Burden of Disease Study 2013 The Lancet 386 9995 743 800 doi 10 1016 S0140 6736 15 60692 4 PMC 4561509 PMID 26063472 a href Template Cite journal html title Template Cite journal cite journal a author1 has generic name help CS1 maint numeric names authors list link a b c d e Knol AB Petersen AC van der Sluijs JP Lebret E 1 January 2009 Dealing with uncertainties in environmental burden of disease assessment Environmental Health 8 1 21 doi 10 1186 1476 069X 8 21 PMC 2684742 PMID 19400963 Briggs D 1 December 2003 Environmental pollution and the global burden of disease British Medical Bulletin 68 1 1 24 doi 10 1093 bmb ldg019 PMID 14757707 Pega Frank Nafradi Balint Momen Natalie Ujita Yuka Streicher Kai Pruss Ustun Annette Technical Advisory Group 2021 Global regional and national burdens of ischemic heart disease and stroke attributable to exposure to long working hours for 194 countries 2000 2016 A systematic analysis from the WHO ILO Joint Estimates of the Work related Burden of Disease and Injury Environment International 154 106595 doi 10 1016 j envint 2021 106595 ISSN 0160 4120 PMC 8204267 PMID 34011457 a b Martin J Prince Fan Wu Yanfei Guo Luis M Gutierrez Robledo Martin O Donnell Richard Sullivan Salim Yusuf 2015 The burden of disease in older people and implications for health policy and practice The Lancet 385 9967 549 62 doi 10 1016 S0140 6736 14 61347 7 PMID 25468153 S2CID 1598103 World Health Organization WHO 2004 Disease incidence prevalence and disability PDF The Global Burden of Disease Retrieved 2009 01 30 Vos T Dec 15 2012 Years lived with disability YLDs for 1160 sequelae of 289 diseases and injuries 1990 2010 a systematic analysis for the Global Burden of Disease Study 2010 Lancet 380 9859 2163 96 doi 10 1016 S0140 6736 12 61729 2 PMC 6350784 PMID 23245607 a b About the Global Burden of Disease GBD project Health statistics and health information systems World Health Organization Archived from the original on October 27 2008 a b Global burden of disease World Health Organization a b c d Standard DALYs 3 discounting age weights WHO subregions XLS Disease and injury regional estimates for 2004 World Health Organization a b c d Standard DALYs 3 discounting age weights WHO subregions YLL XLS Disease and injury regional estimates for 2004 World Health Organization a b What is the environment in the context of health PDF Environmental burden of disease series World Health Organization Pega Frank Nafradi Balint Momen Natalie Ujita Yuka Streicher Kai Pruss Ustun Annette Technical Advisory Group 2021 Global regional and national burdens of ischemic heart disease and stroke attributable to exposure to long working hours for 194 countries 2000 2016 A systematic analysis from the WHO ILO Joint Estimates of the Work related Burden of Disease and Injury Environment International 154 106595 doi 10 1016 j envint 2021 106595 ISSN 0160 4120 PMC 8204267 PMID 34011457 a b Department of Public Health and Environment 2010 Quantification of the disease burden attributable to environmental risk factors PDF Programme on quantifying environmental health impacts World Health Organization Oberg M Jaakkola M S Pruss Ustun A Schweizer C Woodward A 2010 Second hand smoke Assessing the environmental burden of disease at national and local levels PDF Environmental Burden of Disease Series World Health Organization Retrieved January 2 2019 a b c Knol A B Staatsen B A M 8 August 2005 Trends in the environmental burden of disease in the Netherlands 1980 2020 PDF National Institute of Public Health and the Environment Fewtrell Lorna Pruss Ustun Annette Bos Robert Gore Fiona Bartram Jamie 2007 Water sanitation and hygiene quantifying the health impact at national and local levels in countries with incomplete water supply and sanitation coverage PDF WHO Environmental Burden of Disease Series World Health Organization Wyper GM Grant I Fletcher E McCartney G Stockton DL 2019 The impact of worldwide national and sub national severity distributions in Burden of Disease studies A case study of cancers in Scotland PLOS ONE 14 8 e0221026 Bibcode 2019PLoSO 1421026W doi 10 1371 journal pone 0221026 PMC 6688784 PMID 31398232 Wyper GM Grant I Fletcher E Chalmers N McCartney G Stockton DL 2020 Prioritising the development of severity distributions in burden of disease studies for countries in the European region BMC Archives of Public Health 78 3 3 doi 10 1186 s13690 019 0385 6 PMC 6950931 PMID 31921418 Wyper GM Assuncao R Fletcher E Gourley M Grant I Haagsma JA Hilderink H Idavain J Lesnik T von der Lippe E Majdan M McCartney G Santric Milicevic M Pallari E Pires SM Plass D Porst M Santos JV de Haro Moro MT Stockton DL Devleesschauwer B 2021 The increasing significance of disease severity in a burden of disease framework Scandinavian Journal of Public Health 51 2 296 300 doi 10 1177 14034948211024478 PMC 9969303 PMID 34213383 S2CID 235713060 a b Wigmore Cameron 2 November 2007 Study Environmental burden of disease in Canada a b c d e f WHO 2023 Burden of disease attributable to unsafe drinking water sanitation and hygiene 2019 update Geneva World Health Organization 2023 Licence CC BY NC SA 3 0 IGO Call to action on sanitation PDF United Nations Retrieved 15 August 2014 Spears D Ghosh A Cumming O 2013 Open defecation and childhood stunting in India an ecological analysis of new data from 112 districts PLOS ONE 8 9 e73784 Bibcode 2013PLoSO 873784S doi 10 1371 journal pone 0073784 PMC 3774764 PMID 24066070 Johnston R Pruss Ustun A Wolf J 2019 Safer Water Better Health Geneva Switzerland World Health Organization WHO ISBN 978 92 4 151689 1 Gleick P 2002 Dirty Water Estimated Deaths from Water Related Diseases 2000 2020 PDF Report Pacific Institute for Studies in Development Environment and Security Thacker Stephen B Stroup Donna F Carande Kulis Vilma Marks James S Roy Kakoli Gerberding Julie L 2006 Measuring the Public s Health Public Health Reports 121 1 14 22 doi 10 1177 003335490612100107 ISSN 0033 3549 PMC 1497799 PMID 16416694 Garrett Laurie 1 January 2007 The Challenge of Global Health PDF Foreign Affairs 86 January February 2007 14 38 ISSN 0015 7120 Sources edit Lucas Robyn Solar ultraviolet radiation Assessing the environmental burden of disease at national and local levels PDF Environmental burden of disease series Vol 17 World Health Organization Metrics Disability Adjusted Life Year DALY Health statistics and health information systems World Health Organization Metrics Population Attributable Fraction PAF Health statistics and health information systems World Health Organization Archived from the original on November 14 2008 National and regional story Netherlands Environmental burden of disease in Europe the EBoDE project National and regional story European Environment Agency EEA Oberg Mattias Jaakkola Maritta S Woodward Alistair Peruga Armando Pruss Ustun Annette 26 November 2010 Worldwide burden of disease from exposure to second hand smoke a retrospective analysis of data from 192 countries PDF World Health Organization Pruss Annette Havelaar Arie 2001 Fewtrell Lorna Bartram Jamie eds The Global Burden of Disease study and applications in water sanitation and hygiene PDF Water Quality Guidelines Standards and Health London IWA Publishing The WHO guides on assessing the environmental burden of disease PDF World Health Organization Retrieved from https en wikipedia org w index php title Disease burden amp oldid 1188186162, wikipedia, wiki, book, books, library,

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