globalchange  > 气候变化事实与影响
DOI: doi:10.1038/nclimate2121
论文题名:
Climate warming will not decrease winter mortality
作者: Philip L. Staddon
刊名: Nature Climate Change
ISSN: 1758-1414X
EISSN: 1758-7534
出版年: 2014-02-23
卷: Volume:4, 页码:Pages:190;194 (2014)
语种: 英语
英文关键词: Climate-change impacts
英文摘要:

It is widely assumed by policymakers and health professionals that the harmful health impacts of anthropogenic climate change1, 2, 3 will be partially offset by a decline in excess winter deaths (EWDs) in temperate countries, as winters warm4, 5, 6. Recent UK government reports state that winter warming will decrease EWDs7, 8. Over the past few decades, however, the UK and other temperate countries have simultaneously experienced better housing, improved health care, higher incomes and greater awareness of the risks of cold. The link between winter temperatures and EWDs may therefore no longer be as strong as before. Here we report on the key drivers that underlie year-to-year variations in EWDs. We found that the association of year-to-year variation in EWDs with the number of cold days in winter ( <°C), evident until the mid 1970s, has disappeared, leaving only the incidence of influenza-like illnesses to explain any of the year-to-year variation in EWDs in the past decade. Although EWDs evidently do exist, winter cold severity no longer predicts the numbers affected. We conclude that no evidence exists that EWDs in England and Wales will fall if winters warm with climate change. These findings have important implications for climate change health adaptation policies.

Seasonal variation in death rates in temperate countries has long been recognized. EWDs in the UK are defined as the number of deaths from December to March minus the average number of deaths in the preceding August to November, and the following April to July9. Despite fewer cases in northern than southern Europe10, EWDs are causally attributed to seasonal variations in temperature, with low temperatures thought to cause death directly (for example, through hypothermia or falls in icy conditions) and by altering vulnerability to communicable or non-communicable diseases, such as influenza and myocardial infarction, which are more common in winter11. We collated data from the past 60 years to identify key factors associated with the decreasing trend in EWDs in England and Wales, and its year-to-year variation. We deliberately considered a very broad set of factors to minimize the risk of erroneous conclusions. To clarify the thrust of this paper, we are interested in explaining the year-to-year variation in EWDs not the daily variation, and we are not saying that temperature does not play a role, if it did not there would be no EWDs. What we aim to demonstrate is that how harsh a winter is no longer predicts how many EWDs there will be.

Fig. 1 presents relative EWDs and variables identified as possible mediating or causal factors. Between 1951 and 2011, both absolute and year-to-year variation in EWDs declined over time. Three distinct periods in EWD changes were apparent (Supplementary Fig. 1): 1951–1970, where EWDs exhibited very high year-to-year variation and a strongly decreasing overall trend; 1971–2000, where year-to-year variation EWDs halved compared with the preceding period and the decreasing trend continued, albeit less strongly; and 2001–2011, where year-to-year variation was very small and the EWD rate was flat.

Figure 1: Relative excess winter mortality for England and Wales over the past 60 years presented alongside key determinants.
Relative excess winter mortality for England and Wales over the past 60 years presented alongside key determinants.

An index is used to allow for easy comparison in trends and year-to-year variation. Policy initiatives are cold weather payments (CWP), winter fuel payments (WFP) and warm front (WF). EWDs are expressed relative to the size of the population over 65 years old. Before indexation, activity of influenza-like illness was categorized on a scale of 0 to 4, with 0 as baseline and 4 the level of the 1951 epidemic. Housing quality is based on four parameters: inside toilet, hot water, central heating and double glazing. Heating cost is measured as relative to household expenditure.

Data sources and quality.

An initial search of the Web of Knowledge was carried out to identify factors influencing EWD rates. The search encompassed all years and excluded non-English-language articles. Many combinations of search terms were explored (Supplementary Information). Secondary searches were carried out on references cited by articles discussing EWDs and their causes.

Articles relating to the causes of EWDs were identified as targets for data retrieval. These were supplemented by source data: temperature data were obtained from the UK’s Meteorological Office–Hadley Centre Central England Temperature data set30; and economic, social, population and mortality data from the Office for National Statistics. When the required data were unavailable, such as those relating to housing quality or to government initiatives to combat EWDs, a web search using Google was initiated, which was focused on information held in government departments, agencies and other organizations holding specialist housing data sets (Supplementary Information).

Data were collected for the period from 1951 to 2011 and a full list of all data sources used is provided in Supplementary Table 1. Population (and a subset aged over 65 years old), excess winter mortality and incidence of influenza-like illness in England and Wales were documented. Daily mean temperatures for central England were also obtained. These data, being representative of a national geographical mean30, were sufficient for our study of national trends. We therefore collected demographic, EWD, influenza incidence and winter temperature data representative of England and Wales. Certainly different regions will experience different temperatures, but they are all highly correlated to this central England value. Also, EWDs are surprisingly stable across regions, for example with the number of EWDs in Cornwall, the mildest part of England, being nearly identical to that for England and Wales.

A range of extrinsic factors influencing seasonal, temperature-related mortality were also documented. Specific factors were excluded only when their impacts or characteristics were already represented within another factor (for example, income level versus percentage household expenditure on fuel). We recorded expenditure on heating as a percentage of income, policy initiatives aimed at combating EWDs (cold weather payment, winter fuel allowance, warm front) and four key housing quality factors, each focused on a particular housing characteristic affecting health in winter (availability of inside toilet, access to tapped hot water, central heating and double glazing). Data were drawn from the domestic energy fact file, the UK housing energy fact file, the English housing survey and the Halifax housing data set, which contains a reliable description of the changing condition of the UK housing stock. Housing quality improvements were assumed to be linear between available years. This assumption was validated for double glazing, where data for the full period were available. For statistical analyses, all four housing quality measures were combined by simple averaging into a single measure.

Statistical analyses.

EWDs were expressed as a function of population over 65 years old (as about 90% of total EWDs occur in this age group9) to remove changing demographics as a factor. The raw daily temperature data were transformed into two measures: number of days per winter period below 5 °C (a measure of winter cold intensity); and number of days per winter below 5 °C and showing a 4 °C drop from the previous day (a measure of volatility within cold spells, defined as one or more days below 5 °C). Cold days were calculated for the same period as EWDs, namely 1 December to 31 March. Correlation analysis was used to determine the interdependence of variables. Linear multifactor regression analysis identified those factors associated independently with EWDs. This was achieved by carrying out a series of regressions removing the least significant factor at each repeat until only highly significant factors remained. We also ensured that the amount of variation explained by the fitted model, R-square, remained relatively stable. To explain the trend over time in more detail, a moving average method was employed with a period of ten years. This allowed the smoothing of the data to eliminate most of the year-to-year variation. Linear multifactor regression analysis was applied to the smoothed data. To assess year-to-year variation, the relevant data were detrended by removal of the time component and analysed by linear multifactor regression. Using separate data sets, that is, a smoothed data set and a detrended data set, allowed the elimination of confounding time-dependent factors when addressing the two specific questions of: what is causing the long-term trend in decreasing EWDs; and what is causing the short-term year-to-year variation in EWDs. We also tested for correlation breakdown between EWDs and the factors with strong year-to-year variation. To further explain factors associated with EWDs, data were split into subsets characterized by key changes in factors, or the introduction of new factors (such as a policy initiative).

  1. Costello, A. et al. Managing the health effects of climate change: Lancet and University College London Institute for Global Health Commission. Lancet 373, 16931733 (2009).
  2. Patz, J. A., Campbell-Lendrum, D., Holloway, T. & Foley, J. A. Impact of regional climate change on human health. Nature 438, 310317 (2005).
  3. Altizer, S., Ostfeld, R. S., Johnson, P. T. J., Kutz, S. & Harvell, C. D. Climate change and infectious diseases: From evidence to a predictive framework. Science 341, 514519 (2013).
  4. Stern, N. The Economics of Climate Change. The Stern Review (Cambridge Univ. Press, (2007).
  5. McMichael, T., Montgomery, H. & Costello, A. Health risks, present and future, from global climate change. BMJ 344, e1359 (2012).
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  7. HPA Health Effects of Climate Change in the UK 2012 (Health Protection Agency), 2012; http://www.hpa.org.uk/hecc2012 (accessed 05/02/13)
  8. CCRA The UK Climate Change Risk Assessment 2012. (Department for Environment, Food and Rural Affairs, 2012; http://www.nature.com/nclimate/journal/v4/n3/full/www.defra.gov.uk/environment/climate/government/risk-assessment/ (accessed 05/02/13))
  9. ONS Excess Winter Mortality in England and Wales, 1950/51 to 2009/10. (Office for National Statistics, 2010)
  10. Analitis, A. et al. Effects of cold weather on mortality: results form 15 European cities within PHEWE project. Am. J. Epidemiol. 168, 13971408 (2008).
  11. Keatinge, W. R. et al. Cold exposure and winter mortality from ischaemic heart disease, cerebrovascular disease, respiratory disease, and all causes in warm and cold regions of Europe. Lancet 349, 13411346 (1997).
  12. Carson, C., Hajat, S., Armstrong, B. & Wilkinson, P. Declining vulnerability to temperature-related mortality in London over the 20th century. Am. J. Epidemiol. 164, 7784 (2006).
  13. Healy, J. D. Excess winter mortality in Europe: a cross country analysis identifying key risk factors. J. Epidemiol. Comm. Health 57, 784789 (2003). URL:
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资源类型: 期刊论文
标识符: http://119.78.100.158/handle/2HF3EXSE/5234
Appears in Collections:气候变化事实与影响
科学计划与规划
气候变化与战略

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Philip L. Staddon. Climate warming will not decrease winter mortality[J]. Nature Climate Change,2014-02-23,Volume:4:Pages:190;194 (2014).
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