Temporal extrapolation methods

From Opasnet
Jump to: navigation, search
The text on this page is taken from an equivalent page of the IEHIAS-project.

One of the easiest ways of obtaining approximate estimates of future (or past) conditions is by extrapolating the data we do have over time. Thus, if we want to make a 'rough-and-ready' assessment of future levels of contaminants in drinking waters for a period 20 years ahead, we can extrapolate the trend from the last 20 years or so forward. Similarly, if we need to estimate the background prevalence of smoking, or lung cancer, in the years ahead, we can do so by calculating the trend over recent years and projecting this into the future.

Extrapolations of this type can be done using more of less sophisticated methods. In many cases (especially in areas of marketing and business management), it has traditionally been done using judgemental methods - for example by looking at recent data and intuitively estimating what this implies for the future. Rule-based methods can also be used, by applying a set of predefined principles or expectations based on prior understanding of the system, together with recent data, to interpret future developments. In addition, and more objectively, trends can be derived statistically, using regression or related (e.g. autoregressive or Bayesian) methods.

Whatever method is used, care is essential in extrapolation because of the numerous uncertainties involved. Any extrapolation procedure, for example, is based on the assumption that there is valid information in past data and knowledge, and thus that the future is conditioned by the same (or similar) factors to those that have operated previously. While this may be true for business-as-usual scenarios, it clearly is less valid if we are trying to estimate future conditions in the context of new policies or technologies. The amount of information available in the historic record also depends on the length of that record and the accuracy of the data. In some cases it has been suggested that greater weight should be attached to more recent data, both because this is likely to be more accurate and more relevant to current conditions. Nevertheless this can have dangers, especially if there are large, random, short-term variations in the data, which mean that any apparent short-term trend is relatively uninformative. Likewise, the possibility of non-linear (including cyclic or seasonal) variations needs to be recognised, especially when making long-term extrapolations; these are often detectable only with relatively long runs of data.

In the light of these considerations, many analysts have used a combination of autoregressive and moving average functions, in what are known as ARMA (or ARIMA) models. In order to ensure rigour in the way these are applied, the so-called Box-Jenkins methodology is often followed; this defines an explicit set of methods and checks to deal with the uncertainties involved. Nevertheless, there is considerable research in the field of forecasting to show that sophisticated statistical methods do not always out-perform simpler approaches. In the end it seems apparent that the best extrapolations tend to be achieved when prior knowledge about the causal processes operating within the system is combined with robust statistical techniques - and when these are supported by equally robust time series data.

In making extrapolations, therefore, we should alwaysd bear in mind that:

A trend is a trend is a trend,
But the question is, will it bend?
Will it alter its course
Through some unforeseen force
And come to a premature end?
Cairncross (1969), quoted in Armstrong (2001).

References

See also

Integrated Environmental Health Impact Assessment System
IEHIAS is a website developed by two large EU-funded projects Intarese and Heimtsa. The content from the original website was moved to Opasnet.
Topic Pages
Toolkit
Data

Boundaries · Population: age+sex 100m LAU2 Totals Age and gender · ExpoPlatform · Agriculture emissions · Climate · Soil: Degredation · Atlases: Geochemical Urban · SoDa · PVGIS · CORINE 2000 · Biomarkers: AP As BPA BFRs Cd Dioxins DBPs Fluorinated surfactants Pb Organochlorine insecticides OPs Parabens Phthalates PAHs PCBs · Health: Effects Statistics · CARE · IRTAD · Functions: Impact Exposure-response · Monetary values · Morbidity · Mortality: Database

Examples and case studies Defining question: Agriculture Waste Water · Defining stakeholders: Agriculture Waste Water · Engaging stakeholders: Water · Scenarios: Agriculture Crop CAP Crop allocation Energy crop · Scenario examples: Transport Waste SRES-population UVR and Cancer
Models and methods Ind. select · Mindmap · Diagr. tools · Scen. constr. · Focal sum · Land use · Visual. toolbox · SIENA: Simulator Data Description · Mass balance · Matrix · Princ. comp. · ADMS · CAR · CHIMERE · EcoSenseWeb · H2O Quality · EMF loss · Geomorf · UVR models · INDEX · RISK IAQ · CalTOX · PANGEA · dynamiCROP · IndusChemFate · Transport · PBPK Cd · PBTK dioxin · Exp. Response · Impact calc. · Aguila · Protocol elic. · Info value · DST metadata · E & H: Monitoring Frameworks · Integrated monitoring: Concepts Framework Methods Needs
Listings Health impacts of agricultural land use change · Health impacts of regulative policies on use of DBP in consumer products
Guidance System
The concept
Issue framing Formulating scenarios · Scenarios: Prescriptive Descriptive Predictive Probabilistic · Scoping · Building a conceptual model · Causal chain · Other frameworks · Selecting indicators
Design Learning · Accuracy · Complex exposures · Matching exposure and health · Info needs · Vulnerable groups · Values · Variation · Location · Resolution · Zone design · Timeframes · Justice · Screening · Estimation · Elicitation · Delphi · Extrapolation · Transferring results · Temporal extrapolation · Spatial extrapolation · Triangulation · Rapid modelling · Intake fraction · iF reading · Piloting · Example · Piloting data · Protocol development
Execution Causal chain · Contaminant sources · Disaggregation · Contaminant release · Transport and fate · Source attribution · Multimedia models · Exposure · Exposure modelling · Intake fraction · Exposure-to-intake · Internal dose · Exposure-response · Impact analysis · Monetisation · Monetary values · Uncertainty
Appraisal